WO2011019304A2 - Method for immobilizing cells of microorganisms into a sorbent used for oil pollution cleanup - Google Patents
Method for immobilizing cells of microorganisms into a sorbent used for oil pollution cleanup Download PDFInfo
- Publication number
- WO2011019304A2 WO2011019304A2 PCT/RU2010/000479 RU2010000479W WO2011019304A2 WO 2011019304 A2 WO2011019304 A2 WO 2011019304A2 RU 2010000479 W RU2010000479 W RU 2010000479W WO 2011019304 A2 WO2011019304 A2 WO 2011019304A2
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- WO
- WIPO (PCT)
- Prior art keywords
- sorbent
- oil
- immobilizing
- cells
- biosorbent
- Prior art date
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- 239000002594 sorbent Substances 0.000 title claims abstract description 90
- 238000000034 method Methods 0.000 title claims abstract description 53
- 244000005700 microbiome Species 0.000 title claims abstract description 26
- 230000003100 immobilizing effect Effects 0.000 title claims abstract description 14
- 230000002209 hydrophobic effect Effects 0.000 claims abstract description 19
- 239000000443 aerosol Substances 0.000 claims abstract description 18
- 239000000203 mixture Substances 0.000 claims abstract description 17
- 238000004140 cleaning Methods 0.000 claims abstract description 16
- 230000000813 microbial effect Effects 0.000 claims abstract description 16
- 239000002245 particle Substances 0.000 claims abstract description 13
- 239000003209 petroleum derivative Substances 0.000 claims abstract description 6
- 239000000356 contaminant Substances 0.000 claims description 7
- 238000002156 mixing Methods 0.000 claims description 7
- 239000003415 peat Substances 0.000 claims description 6
- 238000000746 purification Methods 0.000 claims description 5
- 230000006378 damage Effects 0.000 claims description 4
- 229920006395 saturated elastomer Polymers 0.000 claims description 3
- 239000012531 culture fluid Substances 0.000 claims description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 14
- 238000004519 manufacturing process Methods 0.000 abstract description 12
- 239000002689 soil Substances 0.000 abstract description 6
- 239000003124 biologic agent Substances 0.000 abstract description 5
- 239000000839 emulsion Substances 0.000 abstract description 2
- 239000003208 petroleum Substances 0.000 abstract 1
- 239000003921 oil Substances 0.000 description 65
- 239000002028 Biomass Substances 0.000 description 12
- 239000000126 substance Substances 0.000 description 12
- 239000007788 liquid Substances 0.000 description 7
- 239000008187 granular material Substances 0.000 description 6
- IXPNQXFRVYWDDI-UHFFFAOYSA-N 1-methyl-2,4-dioxo-1,3-diazinane-5-carboximidamide Chemical compound CN1CC(C(N)=N)C(=O)NC1=O IXPNQXFRVYWDDI-UHFFFAOYSA-N 0.000 description 5
- 239000011148 porous material Substances 0.000 description 5
- 235000010413 sodium alginate Nutrition 0.000 description 5
- 239000000661 sodium alginate Substances 0.000 description 5
- 229940005550 sodium alginate Drugs 0.000 description 5
- 239000003102 growth factor Substances 0.000 description 4
- 241000233866 Fungi Species 0.000 description 3
- 208000012868 Overgrowth Diseases 0.000 description 3
- 229940072056 alginate Drugs 0.000 description 3
- 229920000615 alginic acid Polymers 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 241000194110 Bacillus sp. (in: Bacteria) Species 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 2
- 241000896533 Gliocladium Species 0.000 description 2
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 238000006065 biodegradation reaction Methods 0.000 description 2
- 229910001424 calcium ion Inorganic materials 0.000 description 2
- 239000000969 carrier Substances 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 238000006116 polymerization reaction Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 1
- 240000008042 Zea mays Species 0.000 description 1
- 235000005824 Zea mays ssp. parviglumis Nutrition 0.000 description 1
- 235000002017 Zea mays subsp mays Nutrition 0.000 description 1
- 241000227149 Zoogloea sp. Species 0.000 description 1
- 230000032683 aging Effects 0.000 description 1
- 238000007605 air drying Methods 0.000 description 1
- 239000002199 base oil Substances 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 235000011148 calcium chloride Nutrition 0.000 description 1
- 239000012876 carrier material Substances 0.000 description 1
- 235000005822 corn Nutrition 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- -1 for example Substances 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 230000002538 fungal effect Effects 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000002480 mineral oil Substances 0.000 description 1
- 235000010446 mineral oil Nutrition 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 239000012053 oil suspension Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 238000005067 remediation Methods 0.000 description 1
- 102220201851 rs143406017 Human genes 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 239000002569 water oil cream Substances 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/26—Processes using, or culture media containing, hydrocarbons
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
- C02F3/348—Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed
-
- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K3/00—Materials not provided for elsewhere
- C09K3/32—Materials not provided for elsewhere for absorbing liquids to remove pollution, e.g. oil, gasoline, fat
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G25/00—Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
- C10G25/003—Specific sorbent material, not covered by C10G25/02 or C10G25/03
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G32/00—Refining of hydrocarbon oils by electric or magnetic means, by irradiation, or by using microorganisms
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N11/00—Carrier-bound or immobilised enzymes; Carrier-bound or immobilised microbial cells; Preparation thereof
- C12N11/02—Enzymes or microbial cells immobilised on or in an organic carrier
-
- 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
- C02F1/681—Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water by addition of solid materials for removing an oily layer on water
Definitions
- the invention relates to the field of biotechnology, creating tools for cleaning the environment.
- a new industrial method is proposed for immobilizing microorganism cells into a sorbent used to clean oil-contaminated soils and water areas.
- the use of biosorbent obtained by the claimed method allows the cleaning of large areas of the water surface, marshy areas and land areas from the effects of oil spills, including thin rainbow films.
- Biosorbent is a sorbent carrier with immobilized microorganisms, oil destructors. Processing the oil slick with a biosorbent blocks its further distribution (the effect of physicochemical booms), which makes it possible to collect more than 90% of this pollutant. Biodegradation practically solves the issue of utilization of sorbents after use, which greatly simplifies their use.
- a method of manufacturing a biosorbent according to RU (11) 2299181 (13) C2 (51) IPC C02F 3/34 (2006.01) C12N 1/26 (2006.01) C12R 7/77 (2006.01) Cl 2R 1/645 (2006.01) "BIOCOPBEHT FOR WATER SURFACE CLEANING FROM OIL AND OIL PRODUCTS)), consists in immobilizing the biomass of the strains of micromycete Fusrium lateritium HK-204 or Gliocladium into a hydrophobic sorbent of oil
- deliquesseps HK-205 or Gliocladium delicepseps HK-206 or a consortium of these strains through the overgrowth of mycelium fungi sorbent placed on a nutrient medium.
- the sorbent is made of a hydrophobic oil sorbent based on peat.
- the fungal mycelium is 20-50% by dry weight.
- a disadvantage of the above described methods for producing biosorbents is that the process of obtaining the above biosorbent is intermittent, depending on the time of sorbent fouling with the fungi. Hydrophobic sorbent overgrowth with biomass requires additional reactors in which special conditions are maintained, additional drying chambers of hundreds of square meters in size, because the above methods for producing biosorbents were carried out in laboratory conditions in a small volume and are not suitable for industrial production.
- the method for producing a biological product specified in this patent is that the carrier substance, the microorganism growth factor substance, and the biomass of oil-degrading microorganisms immobilized by dispersing the biomass of the oil-degrading microorganisms in the mass of the carrier material with their physical connection with the carrier substance.
- a carrier substance a composition of Ca-alginate was used.
- the mixture with sodium alginate and suspended biomass in equal volumes is mixed by means of a homogenizer for 2-3 minutes, then pumped through a nozzle into the zone of exposure to the air stream supplied to the ejection area, for example, to form granules from 0.18 to 0.55 mm at a rate of 0.002 m 3 / min.
- Drops formed by the action of an air jet on a mixture jet fall into an aqueous solution containing Ca ions (for example, a 2% aqueous solution of CaCl2), where, due to the chemical combination of calcium ions with sodium alginate and polymerization during aging (for example, for 30 minutes), the formation of drops of Ca-alginate gel, they acquire the properties of a separate body and become granules.
- the granules thus obtained are carriers of the dispersed suspended biomass of immobilized oil-degrading microorganisms and where the composition of the carrier is a composition of Ca-alginate gel, n-alkanes with C HC 16 and substances - growth factor.
- the granules are filtered, washed and placed in saline.
- biological products where the biological agent is prepared in the form of a water-oil suspension, which ensures quick contact of the biological product with oil products and liquids with oleophilic properties, for example, see RF patent N ° 2180276 Cl from
- the challenge facing the developers of the proposed method is to develop industrially suitable high-performance method, providing the manufacture of high-quality oleophilic biosorbent, incorporating microorganisms - oil destructors, hereinafter - bioagents.
- a method of immobilizing microorganism cells into a hydrophobic oleophilic sorbent used to clean oil contaminants consists in mixing two aerosols until the sorbent is saturated with a bioagent.
- the first aerosol consists of a gaseous medium in which sorbent particles are suspended.
- the second aerosol consists of a gaseous medium in which a mixture of either oil or a petroleum product and a culture fluid with a bioagent is suspended.
- An oil or oil aerosol contains, respectively, an oil or oil base mixed with a culture liquid with microbial oil-destructive cells with a biotiter of 10 9 - 10 10 KOE / ml, which ensures the destruction of oil products absorbed subsequently
- the chamber create a mixture of sorbent and oil or oil, non-toxic to the used microorganisms (carriers of biomass of microbial cell strain-oil destructors), aerosols.
- Aerosol is a dispersed system consisting of small solid or liquid particles suspended in a gaseous medium (usually in air).” (See - Wikipedia).
- Sorbent particles have a size of 1 ⁇ 3 mm in diameter.
- any hydrophobic oleophilic sorbent for example, peat sorbent or organomineral sorbent, can be used.
- the technical result of the claimed invention is the creation of an industrial method of immobilization of various bioagents on various hydrophobic oleophilic sorbents, in which it is possible to carry out the process of saturation of the sorbent with bioagents to the required level of bioagent in the sorbent.
- This method is universal for various hydrophobic oleophilic sorbents, because can be used to immobilize any oil-degrading bioagents in various hydrophobic oleophilic sorbents. Given result
- an aerosol consisting of an oil or oil emulsion containing microorganisms-oil destructors.
- the basis of the proposed method is the property of an oleophilic sorbent to sorb oil or oil. Due to the fact that the sorbent has a porous structure with pore sizes from 100 to 300 ⁇ m, aerosol droplets, the size of which can be from 15 to 25 ⁇ m, fall on the surface of the sorbent particles, partially settle on its surface and partially penetrate inside its pores. Together with the oleophilic base, bioagents-oil destructors fall on the surface of the sorbent and in its pores.
- the particle size of the sorbent may lie in the range from 1 to 3 mm in diameter.
- the size of various microorganisms-oil destructors can be from 0.9 to 15 microns, which allows them to be in the composition of aerosol drops and enter the pores of the sorbent.
- the particles of the sorbent become slightly heavier. The sorption ability of the obtained biosorbent almost does not decrease compared to the initial sorbent.
- biosorbents obtained by the method according to this invention sorption and utilization of oil and / or oil products from the surface being cleaned are carried out simultaneously.
- Biosorbents obtained by the present method are characterized by high biodegradation activity in the elimination and intense pollution and thin rainbow films.
- hydrophobic peat sorbent SORBONAFT (TU 0392-001-55763877-2003) was chosen for the production of biosorbent.
- Sorbent obtained by the method described in the patent of the Russian Federation N ° 2336125.
- a composition of environmentally friendly hydrophobic peat mineral oil sorbent is developed under the name
- Biosorbonaft It includes an oleophilic hydrophobic sorbent - Copbonft - 99% and a water-oil emulsion of microorganisms-oil destructors - 1%.
- the maximum absorption capacity of the sorbent for the reference oil product is 650%, the particle size of the bulk sorbent is 1 - 3.0 mm.
- This sorbent has a porous structure, well adsorbs oil 350 - 800%, diesel 300-350%.
- strains that ensure the destruction of petroleum products - one or more strains of microbial cells ZOOGLOEA SP. 14H, ARTNOVASTER SP. 13H, ARTNOVASTER SP. 15H,
- BACILLUS SP. ZN BACILLUS SP. 12 H USED FOR REMEDIATION OF RESERVOIRS AND SOILS CONTAMINATED BY OIL AND OIL PRODUCTS, OR ASSOCIATION OF STRAINS
- oil from the Usinsky field is selected as a carrier of biomass of strains of microbial cells-oil destructors.
- an organomineral sorbent is selected as the sorbent.
- the inventive method allows you to change the components used to obtain biosorbent.
- the method is economical and simple, does not require complex equipment and high costs in mass production.
- Mixing of aerosols can be carried out by known means — using pneumatic sprayers for a sorbent and a spray for liquids connected to sorbent and liquid dispensers.
- the inventive method is controllable - the process of saturation of the sorbent with nutrients is controllable due to what is performed in the chamber, while the time of mixing the aerosols and the conditions of the saturation process — air flow intensity, temperature, humidity, pressure in the chamber — are first experimentally selected and then kept constantly. Microbial cell saturation of oil or oil products is also a controlled process.
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Microbiology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- General Engineering & Computer Science (AREA)
- Biochemistry (AREA)
- Biomedical Technology (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- General Health & Medical Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Biodiversity & Conservation Biology (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Medicinal Chemistry (AREA)
- Tropical Medicine & Parasitology (AREA)
- Virology (AREA)
- Public Health (AREA)
- Materials Engineering (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Processing Of Solid Wastes (AREA)
- Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
- Removal Of Floating Material (AREA)
Abstract
Description
Способ иммобилизации клеток микроорганизмов в сорбент, используемый для очистки нефтезагрязнений The method of immobilization of microorganism cells in a sorbent used to clean oil pollution
Область техники Technical field
Изобретение относится к области биотехнологии, создающей средства для очистки окружающей среды. Предлагается новый промышленный способ иммобилизации клеток микроорганизмов в сорбент, используемый для очистки нефтезагрязненных почв и акваторий. Применение биосорбента, получаемого заявляемым способом, позволяет осуществлять очистку больших пространств водной поверхности, болотистых участков и участков суши от последствий разливов нефтепродуктов, в том числе и тонких радужных пленок. The invention relates to the field of biotechnology, creating tools for cleaning the environment. A new industrial method is proposed for immobilizing microorganism cells into a sorbent used to clean oil-contaminated soils and water areas. The use of biosorbent obtained by the claimed method allows the cleaning of large areas of the water surface, marshy areas and land areas from the effects of oil spills, including thin rainbow films.
Биосорбент - это сорбент-носитель с иммобилизованными микроорганизмами нефтедеструкторами. Обработка нефтяного пятна биосорбентом блокирует его дальнейшее распространение (эффект физико-химических бонов), что позволяет собрать более 90 % этого загрязнителя. Биоразложение практически решает вопрос утилизации сорбентов после использования, что существенно упрощает их применение. Biosorbent is a sorbent carrier with immobilized microorganisms, oil destructors. Processing the oil slick with a biosorbent blocks its further distribution (the effect of physicochemical booms), which makes it possible to collect more than 90% of this pollutant. Biodegradation practically solves the issue of utilization of sorbents after use, which greatly simplifies their use.
Сейчас в мире производится или используется для ликвидации разливов нефти около двух сотен различных сорбентов, которые подразделяются на: неорганические, природные органические и органоминеральные, а также синтетические. Такое большое количество различных видов сорбентов свидетельствует о неудовлетворенности потребителей качеством известных сорбентов и поиском новых видов, удовлетворяющих соотношению «цeнa- кaчecтвo». Качество сорбентов определяется главным образом их емкостью по отношению к нефти, степенью гидрофобности (ненамокаемости в воде), плавучестью после сорбции нефти, возможностью десорбции нефти и регенерации или утилизации сорбента. Now in the world about two hundred different sorbents are produced or used to eliminate oil spills, which are divided into: inorganic, natural organic and organomineral, as well as synthetic. Such a large number of different types of sorbents indicates the dissatisfaction of consumers with the quality of known sorbents and the search for new species that satisfy the “price-ratio” ratio. The quality of sorbents is determined mainly by their capacity with respect to oil, the degree of hydrophobicity (not soaking in water), buoyancy after oil sorption, the possibility of oil desorption and regeneration or utilization of the sorbent.
Предшествующий уровень техники State of the art
Существуют следующие способы иммобилизации биогента на сорбенте-носителе. The following methods for immobilizing a biogen on a sorbent carrier are available.
1. Механическое смешение сорбента и биоагента. 1. Mechanical mixing of sorbent and bioagent.
Недостаток данного способа в том, что при нанесении данного сорбента на поверхность воды происходит разделение сорбента и биоагента. Биосорбент, полученный таким способом, эффективен только для очистки почвы. The disadvantage of this method is that when applying this sorbent to the surface of the water, the sorbent and the bioagent are separated. The biosorbent obtained in this way is effective only for cleaning the soil.
2. Способ получения биосорбента, описанный в патенте RU (11) 2299181 (13) C2(51) МПК C02F З/34 (2006.01) C12N 1/26 (2006.01) Cl 2R 1/77 (2006.01) Cl 2R 1/645 2. The method of producing biosorbent described in patent RU (11) 2299181 (13) C2 (51) IPC C02F З / 34 (2006.01) C12N 1/26 (2006.01) Cl 2R 1/77 (2006.01) Cl 2R 1/645
(2006.01) «БИOCOPБEHT ДЛЯ ОЧИСТКИ ВОДНОЙ ПОВЕРХНОСТИ ОТ НЕФТИ И. (2006.01) “BIOCOPBEHT FOR CLEANING WATER SURFACE FROM OIL I.
НЕФТЕПРОДУКТОВ)) и аналогичный способ получения биосорбента, описанный в патенте RU (11)2318736, (13) C2, (51) МПК C02FЗ/34 (2006.01), C12N1/26 (2006.01) «БИOCOPБEHT ДЛЯ ОЧИСТКИ ВОДОЕМОВ ОТ НЕФТЕПРОДУКТОВ НА ОСНОВЕ ШТАММОВ БАКТЕРИЙ И ДРОЖЖЕВЫХ ГPИБOB». Способ изготовления биосорбента, согласно RU (11) 2299181 (13) C2(51) МПК C02F 3/34 (2006.01) C12N 1/26 (2006.01) C12R 7/77 (2006.01) Cl 2R 1/645 (2006.01) «БИOCOPБEHT ДЛЯ ОЧИСТКИ ВОДНОЙ ПОВЕРХНОСТИ ОТ НЕФТИ И НЕФТЕПРОДУКТОВ)), заключается в иммобилизации в гидрофобный сорбент нефти биомассы штаммов микромицета Fusаrium lаtеritium HK-204 или Gliосlаdium OF PETROLEUM PRODUCTS)) and a similar method for the production of biosorbent described in patent RU (11) 2318736, (13) C2, (51) IPC C02FЗ / 34 (2006.01), C12N1 / 26 (2006.01) "BIOCOPBEHT FOR PURIFICATION OF WATER BASES FROM BASED OIL PRODUCTS BACTERIA AND YEAST MUSHROOMS. ” A method of manufacturing a biosorbent according to RU (11) 2299181 (13) C2 (51) IPC C02F 3/34 (2006.01) C12N 1/26 (2006.01) C12R 7/77 (2006.01) Cl 2R 1/645 (2006.01) "BIOCOPBEHT FOR WATER SURFACE CLEANING FROM OIL AND OIL PRODUCTS)), consists in immobilizing the biomass of the strains of micromycete Fusrium lateritium HK-204 or Gliocladium into a hydrophobic sorbent of oil
dеliquеsсепs HK-205 или Gliосlаdium dеliquеsсепs HK-206 или консорциума этих штаммов, посредством обрастания мицелием грибов сорбента, помещенного на питательную среду. Далее полученный препарат сушат. Сорбент выполнен из гидрофобного сорбента нефти на основе торфа. Мицелий грибов составляет 20 - 50% по сухому весу. deliquesseps HK-205 or Gliocladium delicepseps HK-206 or a consortium of these strains, through the overgrowth of mycelium fungi sorbent placed on a nutrient medium. Next, the resulting preparation is dried. The sorbent is made of a hydrophobic oil sorbent based on peat. The fungal mycelium is 20-50% by dry weight.
И аналогичный способ получения биосорбента, описанный в патенте RU (11) 2318736, (13) C2, (51) МПК C02FЗ/34 (2006.01), C12N1/26 (2006.01) «БИOCOPБEHT ДЛЯ ОЧИСТКИ ВОДОЕМОВ ОТ НЕФТЕПРОДУКТОВ НА ОСНОВЕ ШТАММОВ БАКТЕРИЙ И ДРОЖЖЕВЫХ ГPИБOB». Данный способ получения биосорбента включает иммобилизацию на нефтяном гидрофобном сорбенте дрожжевых грибов Сапdidа liроlуtiса, Сапdidа guilliеrmопdii, Рiсhiа guilliеrmопdii и культур бактерий Rhоdососсus еrуthrороlis. Аrthrоbасtеr sр. в количестве от 10 до 50 процентов (по сухому весу) посредством обрастания мицелием грибов сорбента с последующей сушкой на воздухе. And a similar method for the production of biosorbent described in patent RU (11) 2318736, (13) C2, (51) IPC C02FЗ / 34 (2006.01), C12N1 / 26 (2006.01) “BIOCOPBEHT FOR PURIFICATION OF WATER BODIES FROM OIL PRODUCTS BASED ON STRAUGE WERE WATER YARRY. GIBOB ". This method of biosorbent production involves the immobilization of the yeast fungi Capdida lirolutis, Capdida guilliermopdii, Pischia guilliermopdii and bacteria cultures Rhodossossus eruthorophoris on an oil hydrophobic sorbent. Arthrobaster sp. in an amount of from 10 to 50 percent (by dry weight) by means of sorbent overgrowth with fungus mycelium, followed by air drying.
Недостатком выше описанных способов получения биосорбентов является и то, ЧТΌ процесс получения вышеуказанного биосорбента прерывный, зависящий от времени обрастания сорбента грибами. Обрастание гидрофобного сорбента биомассой требует дополнительных реакторов, в которых выдерживаются специальные условия, дополнительных сушильных камер размером в сотни квадратных метров, т.к. вышеописанные способы получения биосорбентов осуществлялись в лабораторных условиях в небольшом объеме и не подходят для промышленного производства. A disadvantage of the above described methods for producing biosorbents is that the process of obtaining the above biosorbent is intermittent, depending on the time of sorbent fouling with the fungi. Hydrophobic sorbent overgrowth with biomass requires additional reactors in which special conditions are maintained, additional drying chambers of hundreds of square meters in size, because the above methods for producing biosorbents were carried out in laboratory conditions in a small volume and are not suitable for industrial production.
3. Близким к заявляемому способу является: способ получения биопрепарата для очистки водной среды от загрязнения нефтепродуктами, описанный в патенте РФ N° 2255052 (13) C2 (51) 7 C02FЗ/34, C12N11/04, B01J20/22, B01J20/30, C12N11/04, C12RE01 , C02FЗ/34. С 12Nl 1/04, B01J20/22 «CПOCOБ ОЧИСТКИ ВОДНОЙ СРЕДЫ ОТ ЗАГРЯЗНЕНИЯ НЕФТЕПРОДУКТАМИ И БИОПРЕПАРАТ ДЛЯ ОЧИСТКИ ВОДНОЙ СРЕДЫ ОТ ЗАГРЯЗНЕНИЙ НЕФТЕПРОДУКТ AMИ». Указанный в данном патенте способ получения биопрепарата заключается в том, что вещество носителя, вещество-фактор роста микроорганизмов и биомассу микроорганизмов-нефтедеструкторов, иммобилизованную посредством рассосредоточения биомассы микроорганизмов-нефтедеструкторов в массе вещества носителя с физическим соединением их с веществом носителя. В качестве вещества носителя применена композиция из Са-альгинатного геля, н-алканов с Сн-Сiб и вещества-фактора роста микроорганизмов, при этом физическое соединение микроорганизмов-нефтедеструкторов с веществом носителя осуществлено посредством образования капель из смеси суспензированной биомассы с ингредиентами композиции вещества носителя и полимеризации капель с образованием гранул в водном растворе, содержащем ионы Ca. Для иммобилизации микроорганизмов-нефтедеструкторов посредством рассосредоточения биомассы микроорганизмов-нефтедеструкторов в массе вещества носителя с физическим соединением их с веществом носителя приготавливают 1% водную смесь с альгинатом натрия (например, в количестве 100 мл для упомянутого количества суспензии биомассы), тщательно ее перемешивают и выдерживают в течение 2-3 часов для завершения абсорбции фрагментами альгината натрия. К полученной таким образом смеси с альгинатом натрия добавляют факторы роста, например, кукурузный экстракт в количестве 10 г на 100 мл смеси. Смесь с альгинатом натрия и суспензированной биомассы в равных объемах смешивают посредством гомогенезатора в течение 2-3 минут, далее посредством насоса нагнетают через насадку в зону воздействия воздушной струи, подаваемой в область эжектирования, например для образования гранул от 0,18 до 0,55 мм со скоростью 0,002 м3/мин. Образующиеся при воздействии воздушной струи на струю смеси капли попадают в водный раствор, содержащий ионы Ca (например, 2% водный раствор СаСLг), где вследствие химического соединения ионов кальция с альгинатом натрия и полимеризации в процессе выдержки (например, в течение 30 мин) с образованием в каплях Са-альгинатного геля они приобретают свойства обособленного тела и становятся гранулами. При этом имеет место физическое соединение микроорганизмов- нефтедеструкторов с веществом гранул, а полученные таким образом гранулы являются носителями рассосредоточенной суспендированной биомассы иммобилизованных микроорганизмов-нефтедеструкторов и где в качестве вещества носителя применена композиция из Са-альгинатного геля, н-алканов с С H-C 16 и вещества - фактора роста. Гранулы фильтруют, промывают и помещают в физиологический раствор. 3. Close to the claimed method is: a method of obtaining a biological product for cleaning the aquatic environment from oil pollution, described in RF patent N ° 2255052 (13) C2 (51) 7 C02FЗ / 34, C12N11 / 04, B01J20 / 22, B01J20 / 30, C12N11 / 04, C12RE01, C02FZ / 34. С 12Nl 1/04, B01J20 / 22 “METHOD FOR CLEANING THE WATER MEDIA FROM POLLUTION OF OIL PRODUCTS AND BIOLOGICAL PRODUCT FOR CLEANING THE WATER MEDIA FROM POLLUTION OF AMI OIL PRODUCTS”. The method for producing a biological product specified in this patent is that the carrier substance, the microorganism growth factor substance, and the biomass of oil-degrading microorganisms immobilized by dispersing the biomass of the oil-degrading microorganisms in the mass of the carrier material with their physical connection with the carrier substance. As a carrier substance, a composition of Ca-alginate was used. gel, n-alkanes with Sn-Sib and substance-growth factor of microorganisms, while the physical connection of oil-degrading microorganisms with the carrier substance is carried out by the formation of droplets from a mixture of suspended biomass with the ingredients of the composition of the carrier substance and polymerization of droplets with the formation of granules in an aqueous solution containing Ca. ions To immobilize oil-degrading microorganisms by dispersing the biomass of oil-degrading microorganisms in the mass of the carrier substance with their physical connection with the carrier substance, prepare a 1% aqueous mixture with sodium alginate (for example, in an amount of 100 ml for the mentioned amount of biomass suspension), mix it thoroughly and keep it in 2-3 hours to complete the absorption by fragments of sodium alginate. Growth factors, for example, corn extract in the amount of 10 g per 100 ml of the mixture, are added to the thus obtained mixture with sodium alginate. The mixture with sodium alginate and suspended biomass in equal volumes is mixed by means of a homogenizer for 2-3 minutes, then pumped through a nozzle into the zone of exposure to the air stream supplied to the ejection area, for example, to form granules from 0.18 to 0.55 mm at a rate of 0.002 m 3 / min. Drops formed by the action of an air jet on a mixture jet fall into an aqueous solution containing Ca ions (for example, a 2% aqueous solution of CaCl2), where, due to the chemical combination of calcium ions with sodium alginate and polymerization during aging (for example, for 30 minutes), the formation of drops of Ca-alginate gel, they acquire the properties of a separate body and become granules. In this case, there is a physical connection of oil-degrading microorganisms with the substance of the granules, and the granules thus obtained are carriers of the dispersed suspended biomass of immobilized oil-degrading microorganisms and where the composition of the carrier is a composition of Ca-alginate gel, n-alkanes with C HC 16 and substances - growth factor. The granules are filtered, washed and placed in saline.
Недостатком данного способа является то, что в результате его использования получен биопрепарат, который не является биосорбентом, имеет малый срок нахождения в водной среде - размокает и разлагается. The disadvantage of this method is that as a result of its use, a biological product is obtained, which is not a biosorbent, has a short residence time in the aquatic environment - it soaks and decomposes.
Существуют биопрепараты, где биоагент готовится в виде водно-масляной суспензии, что обеспечивает быстрый контакт биопрепарата с нефтепродуктами и жидкостями, обладающими олеофильными свойствами, например см. патент РФ N° 2180276 Cl от There are biological products where the biological agent is prepared in the form of a water-oil suspension, which ensures quick contact of the biological product with oil products and liquids with oleophilic properties, for example, see RF patent N ° 2180276 Cl from
2001.02.19, «OЛEOФИЛЬHЫЙ БИОПРЕПАРАТ, ИСПОЛЬЗУЕМЫЙ ДЛЯ ОЧИСТКИ 2001.02.19, “OLEOPHILIC BIOLOGICAL PRODUCT USED FOR CLEANING
НЕФТЕЗАГРЯЗНЕННОЙ ПOЧBЫ». OIL-CONTAMINATED GOODS. "
Задача, стоящая перед разработчиками заявляемого способа - разработать промышленно пригодный высокопроизводительный способ, обеспечивающий изготовление олеофильного биосорбента высокого качества, имеющего в своем составе микроорганизмы- нефтедеструкторы, далее по тексту - биоагенты. The challenge facing the developers of the proposed method is to develop industrially suitable high-performance method, providing the manufacture of high-quality oleophilic biosorbent, incorporating microorganisms - oil destructors, hereinafter - bioagents.
Раскрытие изобретения Disclosure of invention
Способ иммобилизации клеток микроорганизмов в гидрофобный олеофильный сорбент, используемый для очистки нефтезагрязнений, заключается в смешивании двух аэрозолей до насыщения сорбента биоагентом. Первый аэрозоль состоит из газовой среды, в которой во взвешенном состоянии находятся частицы сорбента. Второй аэрозоль состоит из газовой среды, в которой во взвешенном состоянии находится смесь или масла, или нефтепродукта и культуральной жидкости с биоаrентом. Масляный или нефтяной аэрозоль содержит, соответственно, масляную или нефтяную основу, смешанную с культуральной жидкостью с микробными клетками-нефтедеструкторами с биотитром 109 - 1010KOE/мл, обеспечивающими разрушение нефтепродуктов, поглощенных в последующем A method of immobilizing microorganism cells into a hydrophobic oleophilic sorbent used to clean oil contaminants consists in mixing two aerosols until the sorbent is saturated with a bioagent. The first aerosol consists of a gaseous medium in which sorbent particles are suspended. The second aerosol consists of a gaseous medium in which a mixture of either oil or a petroleum product and a culture fluid with a bioagent is suspended. An oil or oil aerosol contains, respectively, an oil or oil base mixed with a culture liquid with microbial oil-destructive cells with a biotiter of 10 9 - 10 10 KOE / ml, which ensures the destruction of oil products absorbed subsequently
биосорбентом. biosorbent.
В камере создают смесь из сорбентного и масляного или нефтяного, нетоксичного для используемых микроорганизмов (носителей биомассы штаммов микробных клеток- нефтедеструкторов), аэрозолей. In the chamber create a mixture of sorbent and oil or oil, non-toxic to the used microorganisms (carriers of biomass of microbial cell strain-oil destructors), aerosols.
По определению « Аэрозоль— дисперсная система, состоящая из мелких твёрдых или жидких частиц, взвешенных в газовой среде (обычно в вoздyxe)». (См. - Википедия). By definition, “Aerosol is a dispersed system consisting of small solid or liquid particles suspended in a gaseous medium (usually in air).” (See - Wikipedia).
Для получения аэрозолей используется стандартное оборудование - распылители твердых и жидких веществ, а для задания необходимых объемов - дозаторы. To obtain aerosols, standard equipment is used - sprayers of solid and liquid substances, and dispensers are used to set the required volumes.
Частицы сорбента имеют размер - 1 ÷ 3 мм в диаметре. Sorbent particles have a size of 1 ÷ 3 mm in diameter.
Размер капель масляного или нефтяного аэрозоля 15 ÷ 25 мкм. The size of the droplets of oil or oil aerosol 15 ÷ 25 microns.
Капли масляного или нефтяного аэрозоля попадают на поверхность и в поры гидрофобного сорбента, обеспечивая быстрый контакт и внедрение микробных клеток в разветвленную структуру гидрофобного сорбента. В камере процесс иммобилизации микробных клеток, содержащихся в масле или в нефти, в частицы сорбента продолжают до уровня содержания биоагента - не менее 10 живых клеток на 1 г сорбента. Drops of oil or oil aerosol fall on the surface and in the pores of the hydrophobic sorbent, providing quick contact and the introduction of microbial cells into the branched structure of the hydrophobic sorbent. In the chamber, the process of immobilization of microbial cells contained in oil or in oil into sorbent particles continues until the bioagent content is at least 10 living cells per 1 g of sorbent.
В качестве сорбента может быть использован любой гидрофобный олеофильный сорбент, например торфосорбент или органоминеральный сорбент. As the sorbent, any hydrophobic oleophilic sorbent, for example, peat sorbent or organomineral sorbent, can be used.
Технический результат заявляемого изобретения - Создание промышленного способа иммобилизации различных биоагентов на различных гидрофобных олеофильных сорбентах, при котором возможно вести процесс насыщения сорбента биоагентами до необходимого уровня содержания биоагента в сорбенте. The technical result of the claimed invention is the creation of an industrial method of immobilization of various bioagents on various hydrophobic oleophilic sorbents, in which it is possible to carry out the process of saturation of the sorbent with bioagents to the required level of bioagent in the sorbent.
- Данный способ является универсальным для различных гидрофобных олеофильных сорбентов, т.к. может использоваться для иммобилизации любых нефтедеструктирующих биоагентов в различных гидрофобных олеофильных сорбентах. Данный результат - This method is universal for various hydrophobic oleophilic sorbents, because can be used to immobilize any oil-degrading bioagents in various hydrophobic oleophilic sorbents. Given result
достигается за счет нанесения на гидрофобный олеофильный сорбент, находящийся во взвешенном состоянии, аэрозоля, состоящего из масляной или нефтяной эмульсии, имеющей в своем составе микроорганизмы-нефтедеструкторы. achieved by applying to the hydrophobic oleophilic sorbent, in suspension, an aerosol consisting of an oil or oil emulsion containing microorganisms-oil destructors.
В основу заявляемого способа положено свойство олеофильного сорбента сорбировать масло или нефть. За счет того, что сорбент обладает пористой структурой с размерами пор от 100 до 300 мкм, капли аэрозоля, размер которых может быть от 15 до 25 мкм, попадают на поверхность частиц сорбента, частично оседают на его поверхности и частично проникают вовнутрь его пор. Вместе с олеофильной основой на поверхность сорбента и в его поры попадают биоагенты-нефтедеструкторы. The basis of the proposed method is the property of an oleophilic sorbent to sorb oil or oil. Due to the fact that the sorbent has a porous structure with pore sizes from 100 to 300 μm, aerosol droplets, the size of which can be from 15 to 25 μm, fall on the surface of the sorbent particles, partially settle on its surface and partially penetrate inside its pores. Together with the oleophilic base, bioagents-oil destructors fall on the surface of the sorbent and in its pores.
Размеры частиц сорбента могут лежать в диапазоне от 1-го до 3-х мм в диаметре. Размер различных микроорганизмов-нефтедеструкторов может быть от 0,9 до 15 мкм, что позволяет им находиться в составе капель аэрозоля и попадать в поры сорбента. При насыщении сорбента биоагентом частицы сорбента утяжеляются ненамного. Почти не уменьшается сорбционная способность полученного биосорбента по сравнению с исходным сорбентом. The particle size of the sorbent may lie in the range from 1 to 3 mm in diameter. The size of various microorganisms-oil destructors can be from 0.9 to 15 microns, which allows them to be in the composition of aerosol drops and enter the pores of the sorbent. When the sorbent is saturated with a bioagent, the particles of the sorbent become slightly heavier. The sorption ability of the obtained biosorbent almost does not decrease compared to the initial sorbent.
В биосорбенте, полученном в соответствии с заявляемым способом, имеется стабильно надежная фиксация биоагента на сорбенте, позволяющая использовать биосорбент как для очистки почв, так и для очистки воды. In the biosorbent obtained in accordance with the claimed method, there is a stably reliable fixation of the bioagent on the sorbent, which allows the use of the biosorbent for both soil cleaning and water purification.
С использованием биосорбентов, полученных по способу согласно данного изобретения, осуществляют одновременно сорбцию и утилизацию нефти и/или нефтепродуктов с очищаемой поверхности. Using biosorbents obtained by the method according to this invention, sorption and utilization of oil and / or oil products from the surface being cleaned are carried out simultaneously.
Биосорбенты, полученные по заявляемому способу, характеризуются высокой биодеструкционной активностью при ликвидации и интенсивных загрязнений и тонких радужных пленок. Biosorbents obtained by the present method are characterized by high biodegradation activity in the elimination and intense pollution and thin rainbow films.
Лучшие варианты осуществления изобретения The best embodiments of the invention
Для производства биосорбента был выбран гидрофобный торфяной сорбент - "СОРБОНАФТ" (ТУ 0392-001-55763877-2003). Сорбент получен по способу, описанному в патенте РФ N°2336125. На основе заявляемого способа разработан состав экологически чистого гидрофобного торфоминерального нефтяного сорбента под названием The hydrophobic peat sorbent SORBONAFT (TU 0392-001-55763877-2003) was chosen for the production of biosorbent. Sorbent obtained by the method described in the patent of the Russian Federation N ° 2336125. On the basis of the proposed method, a composition of environmentally friendly hydrophobic peat mineral oil sorbent is developed under the name
"Биосорбонафт". В него входит олеофильный гидрофобный сорбент - «Copбoнaфт» - 99% и водно-масляная эмульсия микроорганизмов-нефтедеструкторов - 1%. Максимальная поглотительная способность сорбента по эталонному нефтепродукту составляет 650%, размер .частиц насыпного сорбента 1 - 3,0 мм. Данный сорбент обладает пористой структурой, хорошо адсорбирует нефть 350 - 800%, дизтопливо 300 -350%. В качестве штаммов, обеспечивающих разрушение нефтепродуктов - один или несколько штаммов микробных клеток ZOOGLOEA SP. 14H, АRТНRОВАСТЕR SP. 13H, АRТНRОВАСТЕR SP. 15H, "Biosorbonaft". It includes an oleophilic hydrophobic sorbent - Copbonft - 99% and a water-oil emulsion of microorganisms-oil destructors - 1%. The maximum absorption capacity of the sorbent for the reference oil product is 650%, the particle size of the bulk sorbent is 1 - 3.0 mm. This sorbent has a porous structure, well adsorbs oil 350 - 800%, diesel 300-350%. As strains that ensure the destruction of petroleum products - one or more strains of microbial cells ZOOGLOEA SP. 14H, ARTNOVASTER SP. 13H, ARTNOVASTER SP. 15H,
BACILLUS SP. ЗН, BACILLUS SP. 12 H, ИСПОЛЬЗУЕМЫХ ДЛЯ РЕМЕДИАЦИИ ВОДОЕМОВ И ПОЧВ, ЗАГРЯЗНЕННЫХ НЕФТЬЮ И НЕФТЕПРОДУКТАМИ, ИЛИ АССОЦИАЦИЯ ШТАММОВ BACILLUS SP. ZN, BACILLUS SP. 12 H USED FOR REMEDIATION OF RESERVOIRS AND SOILS CONTAMINATED BY OIL AND OIL PRODUCTS, OR ASSOCIATION OF STRAINS
МИКРООРГАНИЗМОВ-ДЕСТРУКТОРОВ НА ИХ ОСНОВЕ (Патент на изобретение РФ JVg 2266958). MICROORGANISMS-DESTRUCTORS ON THEIR BASIS (Patent for the invention of the Russian Federation JVg 2266958).
В ' качестве носителя биомассы штаммов микробных клеток-нефтедеструкторов выбрано жидкое масло. B 'as a carrier oil destructors-microbial biomass cells strains selected liquid oil.
В другом варианте исполнения биосорбента - в качестве носителя биомассы штаммов микробных клеток-нефтедеструкторов выбрана нефть Усинского месторождения. In another embodiment of the biosorbent, oil from the Usinsky field is selected as a carrier of biomass of strains of microbial cells-oil destructors.
В третьем варианте исполнения биосорбента - в качестве сорбента выбран органоминеральный сорбент. In the third embodiment of the biosorbent, an organomineral sorbent is selected as the sorbent.
Заявляемый способ позволяет менять компоненты, используемые для получения биосорбента. The inventive method allows you to change the components used to obtain biosorbent.
Промышленная применимость Industrial applicability
Способ экономичен и прост, не требует сложного оборудования и высоких затрат при массовом производстве. Смешивание аэрозолей может выполняться известными средствами - при помощи пневматических распылителей для сорбента и распылителя для жидкостей, соединенных с дозаторами сорбента и жидкости. The method is economical and simple, does not require complex equipment and high costs in mass production. Mixing of aerosols can be carried out by known means — using pneumatic sprayers for a sorbent and a spray for liquids connected to sorbent and liquid dispensers.
Заявляемый способ является управляемым - процесс насыщения сорбента биогентами является управляемым за счет того, что выполняется в камере, при этом время смешивания аэрозолей и условия процесса насыщения - интенсивность воздушных потоков, температуру, влажность, давление в камере сначала подбирают опытным путем и далее выдерживают постоянно. Насыщение микробными клетками масла или нефтепродуктов также процесс контролируемый. The inventive method is controllable - the process of saturation of the sorbent with nutrients is controllable due to what is performed in the chamber, while the time of mixing the aerosols and the conditions of the saturation process — air flow intensity, temperature, humidity, pressure in the chamber — are first experimentally selected and then kept constantly. Microbial cell saturation of oil or oil products is also a controlled process.
Выполнение смешивания в закрытой камере также позволяет обеспечить Mixing in a closed chamber also allows for
экологическую чистоту данного процесса. ecological purity of this process.
При сорбции нефтепродуктов в биосорбент собираемые нефтепродукты смешиваются с имеющимся внутри биосорбента маслом или имеющейся нефтью. Находящиеся внутри микробные клетки беспрепятственно перемещаются в среде масло-нефть или нефть-нефть, при этом часть микробных клеток попадает из сорбента на пятно разлитых нефтепродуктов и разрушает это пятно, находясь вне частицы биосорбента. Биосорбент, вобравший в себя максимальное количество нефтепродуктов, может опуститься на дно водоема. С большой вероятностью имеющиеся внутри биосорбента биоагенты уничтожат отсорбированный нефтепродукт. Оставшись без питания, биоагенты погибнут, и на дне останется слой торфа. When oil products are sorbed into a biosorbent, the collected oil products are mixed with the oil or oil present inside the biosorbent. Inside the microbial cells freely move in the oil-oil or oil-oil environment, while part of the microbial cells from the sorbent gets on the spot of spilled oil products and destroys this spot, being outside the biosorbent particle. The biosorbent, which has absorbed the maximum amount of oil products, can sink to the bottom of the reservoir. It is very likely that bioagents within the biosorbent will destroy the sorbed oil product. Left without food, bioagents will die, and a peat layer will remain at the bottom.
Claims
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RU2009130478/10A RU2420579C2 (en) | 2009-08-11 | 2009-08-11 | Method of immobilising microorganism cells in sorbent used for oil cleaning |
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Cited By (2)
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CN102604924A (en) * | 2012-03-02 | 2012-07-25 | 中国人民解放军海军医学研究所 | Offshore oil degrading microbial inoculum and preparation method thereof |
US8927456B2 (en) | 2013-06-11 | 2015-01-06 | Inkastrans (Canada) Ltd. | Absorbent fibrous granules |
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RU2628692C2 (en) * | 2015-10-06 | 2017-08-21 | Публичное акционерное общество "Транснефть" (ПАО "Транснефть") | Biosorbent for soil and water purification from oil and oil products |
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US3843517A (en) * | 1970-01-08 | 1974-10-22 | Grace W R & Co | Methods for elimination of oil slicks |
RU2031860C1 (en) * | 1991-06-20 | 1995-03-27 | Галина Андреевна Кожанова | Method of water treatment from petroleum pollution |
RU2033975C1 (en) * | 1991-06-28 | 1995-04-30 | Галина Андреевна Кожанова | Method of preparing of bacterial preparation for aqueous medium treatment from petroleum products pollution |
US5260002A (en) * | 1991-12-23 | 1993-11-09 | Vanderbilt University | Method and apparatus for producing uniform polymeric spheres |
US5766907A (en) * | 1995-07-12 | 1998-06-16 | Korea Advanced Institute Of Science & Technology | Method for immobilization of whole microbial cells in calcium alginate capsules |
RU2088725C1 (en) * | 1995-07-24 | 1997-08-27 | Хасанов Ильмер Юсупович | Method of removing oil pollution from water surface |
RU2191753C2 (en) * | 1999-09-27 | 2002-10-27 | Государственный научный центр прикладной микробиологии | Biological preparation for removing crude oil and petroleum products from water and ground |
RU2180276C1 (en) * | 2001-02-19 | 2002-03-10 | Институт экологии и генетики микроорганизмов УрО РАН | Oleophilic biological preparation useful for cleaning oil-polluted soil |
RU2298033C2 (en) * | 2005-04-19 | 2007-04-27 | Институт элементоорганических соединений им. А.Н. Несмеянова РАН (ИНЭОС РАН) | Composition for production of carrier for immobilized carbohydrate cleaving microorganisms, and method for carrier production |
RU2313498C2 (en) * | 2005-08-10 | 2007-12-27 | Институт биологии Коми научного центра Уральского отделения Российской академии наук | Mycosorbent for cleaning oil-polluted water surface |
RU2318736C2 (en) * | 2006-02-10 | 2008-03-10 | Институт биологии Коми научного центра Уральского отделения Российской академии наук | Biological sorbent based on bacterial and yeast fungi strains for cleaning petroleum product-polluted water reservoirs |
RU2319541C2 (en) * | 2006-04-07 | 2008-03-20 | Государственное образовательное учреждение высшего профессионального образования "Кубанский государственный технологический университет" (ГОУВПО "КубГТУ") | Sorbent preparation process |
RU2315655C1 (en) * | 2006-09-20 | 2008-01-27 | Государственное образовательное учреждение высшего профессионального образования "Сибирский государственный технологический университет" | Method of producing polymeric sorbents |
RU2007135663A (en) * | 2007-09-27 | 2009-04-10 | Автономная некоммерческая организация Научно-исследовательский центр "БИОМ" (RU) | METHOD FOR IMMOBILIZING MICRO-ORGANISM CELLS |
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Cited By (2)
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CN102604924A (en) * | 2012-03-02 | 2012-07-25 | 中国人民解放军海军医学研究所 | Offshore oil degrading microbial inoculum and preparation method thereof |
US8927456B2 (en) | 2013-06-11 | 2015-01-06 | Inkastrans (Canada) Ltd. | Absorbent fibrous granules |
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WO2011019304A3 (en) | 2011-04-07 |
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