WO2016008950A1 - Process for bacterially devulcanizing sulphur-vulcanized rubber particles - Google Patents
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- WO2016008950A1 WO2016008950A1 PCT/EP2015/066208 EP2015066208W WO2016008950A1 WO 2016008950 A1 WO2016008950 A1 WO 2016008950A1 EP 2015066208 W EP2015066208 W EP 2015066208W WO 2016008950 A1 WO2016008950 A1 WO 2016008950A1
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- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J11/00—Recovery or working-up of waste materials
- C08J11/04—Recovery or working-up of waste materials of polymers
- C08J11/10—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
- C08J11/105—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with enzymes
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- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms; 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
- C12N1/20—Bacteria; Culture media therefor
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- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms; 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
- C12N1/20—Bacteria; Culture media therefor
- C12N1/205—Bacterial isolates
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- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12P—FERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
- C12P5/00—Preparation of hydrocarbons or halogenated hydrocarbons
- C12P5/007—Preparation of hydrocarbons or halogenated hydrocarbons containing one or more isoprene units, i.e. terpenes
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- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12P—FERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
- C12P5/00—Preparation of hydrocarbons or halogenated hydrocarbons
- C12P5/02—Preparation of hydrocarbons or halogenated hydrocarbons acyclic
- C12P5/026—Unsaturated compounds, i.e. alkenes, alkynes or allenes
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- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2307/00—Characterised by the use of natural rubber
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- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2309/00—Characterised by the use of homopolymers or copolymers of conjugated diene hydrocarbons
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- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2309/00—Characterised by the use of homopolymers or copolymers of conjugated diene hydrocarbons
- C08J2309/06—Copolymers with styrene
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- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2319/00—Characterised by the use of rubbers not provided for in groups C08J2307/00 - C08J2317/00
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- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Definitions
- the invention relates to a new Acidithiobacillus ferrooxidans strain as well as a process for bacterially devulcanizing sulphur-vulcanized rubber particles and devulcanized rubber particles obtainable by said process.
- Processes are known for microbial and enzymatic activation of powdered rubber and rubber granulates.
- EP 1620498 discloses a process for surface activation and/or devulcanisation of sulphur- vulcanised rubber particles.
- the rubber particles are treated in a biotechnoiogical manner in a medium with mesophilic anaerobic and/or mesophilic optionally anaerobic and/or mesophilic micro aerophiiic bacteria and/or with one or more enzyme systems of such bacteria.
- EP0493732 discloses a method for reprocessing scrap rubber, which produces reclaimed rubber from comminuted scrap rubber after devulcanization, in a biotechnology-type of process, by holding the comminuted scrap rubber in a bacterial suspension of chemolithotrophic microorganisms with a supply of air, until sulphur as elementary sulphur and/or sulphuric acid is separated from the remaining replasticized reclaimed rubber.
- This biotechnoiogical reprocessing obtains reclaimed rubber and sulphur in a simplified manner which products can be reused.
- DE 19728036A discloses a process for surface activation and modification of sulphur cross-linked rubber particles by biotechnical treatment in a suspension of the rubber particles, water and biologically active material for breaking the polysuiphidic sulphur bridges and for oxidising the sulphur, by which the treatment is limited to the particle surface and reactive groups in the form of hydroxyl groups, epoxy groups and carboxyl groups are formed over a period of time, the biotechnical treatment being terminated when the concentration of reactive functional groups reaches a maximum.
- thermophilic optionally chemolithotrophic Su lib lob us acidocaldarius is primari ly used as a sulphur oxidizing microorganism and, on the other hand, the treatment of the rubber particles is carried out merely with the enzyme system of this microorganism.
- the rubber particles themselves are not in direct contact with the microorganisms.
- One of the objects of the present invention is to provide an Acidithiobacillus ferrooxidans strain deposited under deposit number DSM 32046.
- Another object of the present invention is to provide a process for aerobic bacterial devulcanization of sulphur- vulcanized rubber particles having a size of 10-2000 micron and wherein said sulphur-vulcanized rubber particles are obtainable by spraying rubber-containing articles with water under pressure and drying said resulting sulphur-vulcanized rubber particles to an initial water content of 0.01 to 20% by weight, the process comprising:
- a further object of the invention is to provide devulcanized rubber particles obtainable by the process of the invention and characterized in that the obtained devulcanized rubber particles are chemically modified and contain sulfoxides and/or sulphur trioxides and/or methyl-assisted conjugated double-bonds and/or hydroxyl-groups and/or carboxyl-groups and/or epoxy groups on the surface of said devulcanized rubber particles.
- Figure 1 shows SEM images of rubber particles obtained by spraying car tyres with water under high pressure. Left: 150x magnification; right: 500x magnification.
- Figure 2 illustrates the FTIR analysis of tyres rubber powder treated with A. ferrooxidans strain DSM 32046. Peak at 3300 cm "1 : hydroxyl groups.
- NT untreated; 48h: treatment for 48h, 6d: treatment for 6 day
- Figure 3 shows the EDX analysis of NR treated for 48h with A. ferrooxidans strain DSM 32046. Untreated and treated values were compared by a Student t-test. ***p ⁇ 0.001
- Figure 4 illustrates the FTIR analysis of tyres rubber powder treated with A. ferrooxidans strain DSM 32046. Peak at 1536 cm “1 : methyl-assisted conjugated double-bonds.
- Figure 5 shows the analysis of sulphur content on rubber particles by by combustion ionic chromatography.
- NT untreated (100%)
- TT treatment with A. thiooxidans
- TF treatment with A. ferrooxidans.
- Rubber is the main raw material used in manufacturing tires, and both natural and synthetic rubber are used. Natural rubber is found as a milky liquid in the bark of the rubber tree, Hevea Brasiliensis. To produce the raw rubber used in tire manufacturing, the liquid latex is mixed with acids that cause the rubber to solidify. Presses squeeze out excess water and form the rubber into sheets, and then the sheets are dried in tall smokehouses, pressed into enormous bales, and shipped to tire factories around the world. Synthetic rubber is produced from the polymers found in crude oil.
- Carbon black is a fine, soft powder created when crude oil or natural gas is burned with a limited amount of oxygen, causing incomplete combustion and creating a large amount of fine soot.
- Sulphur and other chemicals are also used in tires.
- Specific chemicals when mixed with rubber and then heated, produce specific tire characteristics such as high friction (but low mileage) for a racing tire or high mileage (but lower friction) for a passenger car tire.
- Some chemicals keep the rubber flexible while it is being shaped into a tire while other chemicals protect the rubber from the ultraviolet radiation in sunshine. In total, over 200 raw materials go into tire composition.
- the rubber compounds are made up of elastomers, reinforcing fillers, plasticizers and others chemicals elements.
- ATR-FTIR is the abbreviation for Fourier Transform Infrared Spectroscopy coupled to Attenuated Total reflection module.
- Chemolithotrophic bacteria are bacteria able to deriving energy from the oxidation of inorganic compounds of iron, nitrogen, sulphur, or hydrogen.
- An aerobic bacteria is an organism that can survive and grow in an oxygenated environment.
- Devulcanization is the modification of the surface chemistry of rubber particles by bacteria, which cause the reduction of sulphur content on the rubber matrix and the addition of chemical groups, such as hydroxyl groups. Devulcanization occurs when rubber particles are added in the devulcanization media supplemented by the bacteria.
- Devulcanized-rubber particles are rubber particles that were subjected to devulcanization.
- a dienophile is the olefmic or acetylenic component that is seeking a diene in the Diels-Alder reaction.
- EPDM represents ethylene-propylene diene monomer rubber
- NR is the abbreviation of natural rubber. Milky, white latex, containing rubber globules, is obtained by making an incision into the bark of rubber trees, the cultivation of which requires specific climatic conditions and rainfall. Rubber tree plantations are mainly located in
- SBR is the abbreviation of styrene butadiene rubber. 60% of rubber used in the tire industry is synthetic rubber, produced from petroleum-derived hydrocarbons, although natural rubber is still necessary for the remaining 40%. Synthetic elastomers deform under stress and return to their original shape when the stress is removed (hysteresis). This property is extremely valuable for the manufacture of high-grip tires. Synthetic rubber also provides other specific properties, most notably in the areas of longevity and rolling resistance. It's mainly used for passenger car and motorcycle tire as it gives them good grip performances. SEM/EDX represents the abbreviation of scanning electron microscope coupled with an energy dispersive X-ray analysis system.
- the present invention concerns an Acidithiobacillus ferrooxidans strain deposited under deposit number DSM 32046.
- Another object of the invention is to provide a process for aerobic bacterial devulcanization of sulphur- vulcanized rubber particles having a size of 10-2000 micron and wherein said sulphur- vulcanized rubber particles are obtainable or obtained by spraying rubber-containing articles with water under pressure and drying said resulting sulphur-vulcanized rubber particles to an initial water content of 0.01 to 20% by weight, the process comprising:
- the pulverization technique of the present invention is based on high-pressure water or water-jet combined with an optimized culture media allowing a reduction of the to ic chemicals present in the GTR.
- Applicants are able to work with increased concentration of GRT (preferably 20% instead of 5% as presented by Li et al.) and without observing any biomass decrease after rubber addition on bacterial cultures.
- the present invention is based on a specific choice of bacterial species and of growth medium using a combination between iron and sulphur-bonds containing compounds, such as thiosulfate and tetrathionate, increasing the ability of bacteria to use disulphide bonds in GTR as source of energy.
- the devulcanization process of the invention already takes place after 48h of treatment instead of 30 days as described by Li et al.
- the rubber-containing articles are selected from tires or tires segments, tire treads, shoe-soles, conveyor belts.
- the rubber-containing articles also include but are not limited to pneumatic tires, rubber boots, rubber clothing, wet-suits, dry-suits, bumpers, road fenders, marine fenders, rubber dampers, pads for tank tracks, rubber crawler tracks, machine anti- vibration pads, protective rail car liners, noise insulation pads, flooring tiles, rail dampers, boat trailer pads, wind-shield wiper blades, extruded profiles, injection moulding cores, mud flaps.
- Pneumatic tires are used on many types of vehicles, including cars, bicycles, motorcycles, trucks, heavy equipment and aircraft. Solid rubber (or other polymer) tires are used in various non-automotive applications, such as some casters, carts, lawnmowers and wheelbarrows. Heavy duty tires are also referred to as Truck/Bus tires.
- the sulphur-vulcanized rubber particles to be devulcanized are advantageously obtained by spraying rubber-containing articles such as tires or tire segments with water under high pressure and drying the resulting particles.
- the volume of the medium for bacterial growth containing said aerobic chemolithotrophic bacteria that is supplemented to the treatment medium for devulcanization is comprised between 10 to 80%.
- the sulphur-vulcanized rubber particles of Step b) are added at a concentration between 1 and 35% by weight.
- the aerobic chemolithotrophic bacteria of Step a) are employed as a pure strain or in a community.
- the medium for bacterial growth of Step a) and the treatment medium for devulcanization of Step b) are agitated.
- the agitation comprises vertical or horizontal helically agitated mixing in a range of 10 to 300 revolutions per minute (rpm) and/or orbitally shaking in a range of 10 to 500 rpm and/or air insufflation in a range of 0.01 to 20L/min.
- the medium for bacteria culture and growth contains: Na 2 S03, FeS0 4 , FeC and Na 2 S 4 0 6 or their mixtures
- Na 2 SC"3 and/or FeS0 4 in a concentration comprised between 0.05 to 4.0 g/L and/or
- the treatment medium for devulcanization of Step b) further contains dienophiles and organic acids.
- the organic acids are selected among the group of maleic acid, pyruvic acid, benzoic acid, salicylic acid and or their mixtures.
- the dienophiles are selected among the group consisting of maleic anhydride, 2-oxopropanal or their mixtures.
- the medium for bacteria culture and growth may comprise salicylic acid in a concentration comprised between 0, preferably 0.01, to 0.5g/L and/or benzoic acid in a concentration comprised between 0, preferably 0.01, to 0.5 g/L and/or pyruvic acid in a concentration comprised between 0, preferably 0.01, to 0.5 g/L and/or maleic acid in a concentration comprised between 0, preferably 0.01, to 0.5 g/L
- the medium for bacterial growth further comprises at least one optional further constituent selected from: MnS04; Leucine; Thymol; Salicylic acid or their mixtures.
- the pH between 1.0 to 7.0, preferably between 1.5 to 6.5, of the medium for bacteria growth can be regulated by using 1M to 10M HC1, 60% to 98% H 2 S0 4 , 1M to 10M NaOH and 1M to 2M K 2 C0 3 .
- Consumption of the energy source for bacteria growth is monitored by assessing Fe 2+ and/or Fe 3+ concentration by measuring the absorbance of the media at 220-250 nm (Fe 2+ ) and/or 280- 340 nm (Fe 3+ ) and/or by analysis with inductively coupled plasma mass spectrometry (ICP) and/or with Atomic Absorption Spectroscopy (AAS), wherein Na2S 2 C"3 utilization is determined by methylene blue discoloration and/or ion chromatography, and wherein sulphur oxidation is determined by measuring the oxygen consumption by means of a respirometer.
- ICP inductively coupled plasma mass spectrometry
- AAS Atomic Absorption Spectroscopy
- the aerobic chemolithotrophic bacteria of Step a) is the Acidithiobacillus ferrooxidans strain deposited under deposit number DSM 32046 employed as a pure strain or in a community.
- DSM 32046 Dishizadase
- the necessity to culture bacteria separately as a stock of living microorganisms for devulcanization is fundamental for an efficient industrialization of the process.
- contaminations in the rubber powder represents an obstacle for an efficient devulcanization, since the source of contaminations (fungi or other bacteria) may interfere with the growth of the selected bacteria, may degrade the rubber particles and may interfere with the chemical and enzymatic reactions involved in the devulcanization.
- rubber particles are sterilized before and / or after the devulcanization in order to avoid contaminations from bacteria and other microorganisms by ⁇ -sterilization or steam sterilization or chemical sterilization based on ethylene oxide or nitrogen dioxide or ozone.
- the invention provides a process for bacterially devulcanizing sulphur- vulcanized rubber particles having a size of 10-2000 micron, preferably of 10-900 micron, and more preferably a size of 150-600 micron, and an initial moisture content of 0.01 to 20%, preferably of 0.01 to 5% by weight and more preferably of 0.1 to 4%.
- the sulphur- vulcanized rubber particles to be treated can come from many sources.
- the sulphur-vulcanized rubber particles can be obtained by spraying tires or tire segments with water under high pressure and drying the resulting particles.
- the sulphur-vulcanized rubber particles to be devulcanized may be subjected to a preliminary drying treatment to reach the specified initial moisture content.
- sulphur-vulcanized rubber particles can come from a comminution process which does not require a drying treatment.
- rubber particles are sterilized by ⁇ -sterilization steam sterilization before the devulcanization in order to avoid contaminations from bacteria and other microorganisms .
- bacteria are selected from aerobic chemolithotrophic organisms.
- Acidithiobacillus thiooxidans represent 30%> of the community and Acidithiobacillus ferrooxidans represent 30% of the community and Thiobacillus thioparus represent 30%> of the community and Thiobacillus thiophilus represent 10%> of the community.
- the community of bacteria are subject to a culture process to grow the bacteria, in a bacterial growth medium comprising an aqueous solution containing inorganic salts at a pH from 0.5 to 7, preferably from 0.5 to 4.5, and a temperature of 20 to 35°C, preferably from 20 to 30°C, said culture medium further comprising an energy source for promoting bacteria growth, selected from Na 2 S03 and/or FeS0 4 , and/or FeCb and/or Na 2 S 4 0 6 and/or their mixtures.
- the pH of the medium for bacteria growth may be regulated by using 1M to 10M HC1, 60% to 98% H 2 S0 4 , 1M to 10M NaOH and/or 1M to 2M K 2 C0 3 .
- the growth medium can be agitated by different ways. Agitation can be vertical or horizontal helically agitated mixing in a range of 10 to 300 revolutions per minute (rpm), preferably 30 to 100 120 rpm, or orbitally shaking in a range of 10 to 500 rpm, preferably 50 to 200 rpm, or air insufflation in a range of 0.01 to 20L/mn.
- rpm revolutions per minute
- rpm revolutions per minute
- orbitally shaking in a range of 10 to 500 rpm, preferably 50 to 200 rpm
- air insufflation in a range of 0.01 to 20L/mn.
- Consumption of the energy source for bacteria growth is monitored by measuring the absorbance of the media at 220-250 nm (Fe 2+ ) and/or 280-340 nm (Fe 3+ ) or by measuring Fe 2+ to Fe 3+ oxidation colorimetrically or 230-260 nm (Na2S 2 03), wherein Na 2 S 2 03 utilization is determined by iodine titration methylene blue decoloration, and wherein sulphur oxidation is determined by measuring the oxygen consumption by means of a respirometer.
- the rubber particles are then subject to a sulphur devulcanization treatment in a treatment medium comprising the bacteria and containing a concentration of rubber particles between 1 and 35% by weight.
- a treatment medium comprising the bacteria and containing a concentration of rubber particles between 1 and 35% by weight.
- the medium is preferably at a pH from 0.5 to 4.5 and at a temperature of 20 to 30°C.
- the treatment medium comprising the bacteria and containing a concentration of rubber particles between 1 and 35% by weight further contains MgS0 4 in a concentration comprised between 0.05 to 4.0 g/L, preferably between 0.05 to 3.0 g/L, and K 2 HP0 4 in a concentration comprised between 0.05 to 10.0 g/L, preferably between 0.05 and 3.5 g/L, and (NH 4 ) 2 S0 4 in a concentration comprised between 0.05 to 10.0 g/L, preferably between 2.0 to 8.0 g/L.
- This medium may comprise at least one optional further constituent selected from: a. KC1 in a concentration comprised between 0.1 to 2 g/L, and/or b.
- the devulcanization treatment can last for 24 hours to 12 days.
- the resulting devulcanized rubber particles are humid and are dried to a moisture content of 0.01 to 15% by weight.
- rubber particles are sterilized after the devulcanization in order to avoid contaminations from bacteria and other microorganisms by ⁇ -sterilization heating or steam sterilization.
- the devulcanized rubber particles of the invention are defined by the presence of free organic matter in a concentration between 0.1% to 0.5% by weight, the reduction of over 80% of the concentration of volatile compounds such as cyclo hexanone, cyclopropane and ethanol in a NR/SBR mixture (car tires), a reduction of the concentration of Methyl isobutyl ketone (MIBK) of at least 50 % (in car and truck tires), an increased wettability assessed by measuring the reduction of water contact angle in a range between 75% to 95% as well as an increase of water retain in a range between 75% to 150%.
- MIBK Methyl isobutyl ketone
- Water retain was assessed by measuring the percentage of distilled water retained in a defined amount of rubber particles.
- Water contact angle was assessed by measuring the water contact angle of a drop of water on the surface of a rubber compound. A horizontal picture is taken for each drop and the contact angle is measured on the picture.
- MIBK Methyl isobutyl ketone
- Rubber particles are obtained by spraying tyres with water at a rate of between 1 and 4 meters per minute, with water under high-pressure in the range of 800 to 3000 bars, and then dried. These particles are characterized by a high surface area and an irregular shape (figure 1). The particles thus obtained have a size-distribution comprised between 2000 and 50 micrometers.
- a general protocol for the treatment of rubber particles with selected bacteria is described below.
- bacteria are maintained in culture with inorganic salt and energetic substrate for promoting their expansion.
- the aqueous media is depleted of the energetic sources in order to promote targeting of sulphured compound present in the rubber. Due to that, bacteria directly use sulphur compound from the rubber particles as a source of energy and this leads to devulcanization of the rubber.
- Acidithiobacillus ferrooxidans strain DSM 32046 are maintained in culture in an aqueous growth media containing 0.5 g/L FeS04, 0.4 g/L MgS0 4 , 0.6 g/L (NH 4 )2S04, 0.4 g/L K 2 HP04, 0.3 g/L K2S406.
- the pH is adjusted with H2S04 at 2.20.
- Bacteria are grown in 500 L bioreactors. When the bacteria count reaches 1x106 bacteria/mL, 750 L of the bacteria medium from the grown cultures are diluted with devulcanization medium in a ratio of 1 :6 into the devulcanization bioreactor, to reach a final volume of 3 ⁇ 00 L.
- the devulcanization media is composed by 0.6 g/L MgS04, 2 g/L (NH4)2S04, 0.2 g/L KH2P04, 0.5 g/L K2HP04.
- rubber particles composed by NR are added into the devulcanization bioreactor in a concentration of 20% weight/volume (600 kg for 3 ⁇ 00 L).
- the mixture of rubber particles and bacteria is maintained under agitation at 100 rpm at a temperature of 30°C for 48 hours or 6 days.
- rubber particles are separated from the aqueous medium by passing the mixture through a drainer (commercially available), then dried at 120°C in an industrial commercially available installation, to obtain a rubber powder with 1.0 + 0.3 % moisture.
- Treated rubber particles are analysed by ATR-FTIR and by SEM/EDX.
- the ATR-FTIR analysis shows the appearance of hydroxyl groups on the surface of the rubber particles (see Figure 2, broad peak at 3'300 cm-1).
- the intensity of the peak, which is attributable to the quantity of hydroxyl groups, is time depended and increases after 6 days of treatment ( Figure 2).
- the SEM/EDX analysis of the rubber particles after 48h of treatment showed a decrease of sulphur on the surface of the particles and an increase of oxygen, confirming the presence of hydroxyl groups on the surface ( Figure 3).
- Example 2 Two strains of thiobacilli, the A. ferrooxidans strain DSM 32046 and one Acidithiobacillus thiooxidans strain, are grown separately in 15 L bioreactors.
- the growth media for A. ferrooxidans strain is composed by 0.1 g/L FeS04, 0.5 g/L MgS04, 3 g/L (NH4)2S04, 0.5 g/L K2HP04, 2 g/L Na2S203 and 0.05 g/L salicylic acid.
- the pH is adjusted with H2S04 at 4.5.
- the growth medium for ⁇ 4. thiooxidans strain is composed by 0.05 g/L MnS04, 0.5 g/L MgS04, 3.0 g/L (NH4)2S04, 2.0 g/L KH2P04, 2.0 g/L Na2S203 and 0.05 g/L salicylic acid.
- the pH is adjusted with H2S04 at 4.5.
- the devulcanization media for A. ferrooxidans strain is composed by 0.5 g/L MgS04, 3.0 g/L (NH4)2S04, 0.8 g/L KH2P04, 1.0 g/L K2HP04, 0.05 g/L salicylic acid and 0.01 g/L pyruvic acid.
- the devulcanization media for A. thiooxidans strain is composed by 0.5 g/L MgS04, 3.0 g/L (NH4)2S04, 2.0 g/L KH2P04, 1.0 g/L K2HP04, 0.05 g/L salicylic acid and 0.01 g/L pyruvic acid.
- the rubber particles composed by SBR/NR are added into the devulcanization bioreactors in a concentration of 20% weight/volume (6 kg for 30 L).
- the mixture of rubber particles and bacteria is maintained under agitation at 100 rpm at a temperature of 30°C for 48 hours.
- the rubber particles are separated from the aqueous medium by passing the mixture through a drainer (commercially available), then dried at 55°C in an industrial commercially available installation, to obtain a rubber powder with 1.5 + 0.2 % moisture.
- the total sulphur content of the treated particles is analysed by combustion ionic chromatography. A decrease of 16% and of 29% of the total sulphur content in the treated particles is observed after treatment with A. thiooxidans and A. ferrooxidans, respectively ( Figure 5). These results demonstrate that both species are able to reduce the sulphur content on the rubber particles, thus fully able to perform the devulcanization. Moreover, the rubber powder before treatment presents some methyl-assisted conjugated doubles bonds on the surface, which is visible by ATR-FTIR analysis (peak at 1536 cm-1, Figure 5). These chemical structure decrease the mechanical properties of the rubber and the treatment with A. ferrooxidans in the presence of salicylic acid allows the disappearing of these undesired structures (Figure 5). This proves that the bacterial treatment causes the modification of the surface chemistry of the rubber particles and advantageously increases the mechanical properties of the final product.
- HS-GC-MS headspace Gas Chromatography Mass Spectrometry
- the A. ferrooxidans strain DSM 32046 is grown as described in example 2.
- the bacteria count reaches 1x106 bacteria/mL
- 10 L of the bacteria medium from the stock culture are diluted with the devulcanization medium (composition as described in example 2) in a ratio of 1 :3 into the devulcanization bioreactor, to reach a final volume of 30 L.
- rubber particles composed by EPDM are added into the devulcanization bioreactors in a concentration of 10% weight/volume (3 kg for 30 L).
- the mixture of rubber particles and bacteria is maintained under agitation at 100 rpm at a temperature of 30°C for 48 hours.
- the obtained particles are drained and dried as described in example 2, so as to obtain a rubber powder with ⁇ 1.5% moisture.
- Treated and untreated particles were analysed by MEB/EDX and it was shown a decrease of the content of sulphur on the surface of the particles after treatment, evidencing that A. ferrooxidans strain DSM 32046 is able to devulcanize several types of rubbers.
- Example 4 Two strains of thiobacilli, one Thiobacillus thioparus and one Thiobacillus thiophilus, are grown separately in 15 L bioreactors.
- the growth media of the T. thioparus is composed by 0.01 g/L MnS04, 0.5 g/L MgS04, 0.1 g/L (NH4)2S04, 4.0 g/L KH2P04, 2.0 g/L K2HP04, 0.15 g/L FeC13 and 5.0 g/L Na2S203.
- the pH is adjusted with H2S04 at 6.5.
- the growth media of the T. thiophilus is composed by 0.8 g/L NH4C1, 1.0 g/L MgS04, 0.1 g/L (NH4)2S04, 2.0 g/L KH2P04, 0.2 g/L K2HP04, 0.8 g/L KN03 and 5.0 g/L Na2S203.
- the pH is adjusted with H2S04 at 6.5.
- the devulcanization media for T. thioparus is composed by 0.8 g/L MgS04, 0.25 g/L
- the growth media for T. thiophilus is composed by 0.8 g/L NH4C1, 1.0 g/L MgS04, 0.25 g/L (NH4)2S04, 2.0 g/L KH2P04, 0.5 g/L K2HP04 and 1.0 g/L KN03.
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Priority Applications (16)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AU2015289182A AU2015289182A1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| RS20190111A RS58339B1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| US15/326,852 US11124759B2 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| EP15738346.4A EP3169769B1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| SI201530596T SI3169769T1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| EA201790083A EA033674B1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| BR112017000663-4A BR112017000663B1 (en) | 2014-07-16 | 2015-07-15 | PROCESS TO DEVUCULATE BACTERIALLY SULFUR VULCANIZED RUBBER PARTICULATES |
| PL15738346T PL3169769T3 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| ES15738346T ES2709441T3 (en) | 2014-07-16 | 2015-07-15 | Procedure for bacterial devulcanization of rubber particles vulcanized with sulfur |
| CA2955402A CA2955402C (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| MX2017000693A MX376447B (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| JP2016576038A JP6825918B2 (en) | 2014-07-16 | 2015-07-15 | Method for desulfurizing sulfur vulcanized rubber particles by bacteria |
| EP18195560.0A EP3438244B1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| CN201580038487.5A CN107108951B (en) | 2014-07-16 | 2015-07-15 | Method for bacterial desulfurization of vulcanized rubber particles |
| KR1020177003300A KR102125115B1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| US17/411,812 US20210380933A1 (en) | 2014-07-16 | 2021-08-25 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
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| CH1080/14 | 2014-07-16 | ||
| CH10802014 | 2014-07-16 |
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| US15/326,852 A-371-Of-International US11124759B2 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
| US17/411,812 Division US20210380933A1 (en) | 2014-07-16 | 2021-08-25 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
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| PCT/EP2015/066208 Ceased WO2016008950A1 (en) | 2014-07-16 | 2015-07-15 | Process for bacterially devulcanizing sulphur-vulcanized rubber particles |
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| US (2) | US11124759B2 (en) |
| EP (2) | EP3438244B1 (en) |
| JP (1) | JP6825918B2 (en) |
| KR (1) | KR102125115B1 (en) |
| CN (1) | CN107108951B (en) |
| AU (1) | AU2015289182A1 (en) |
| BR (1) | BR112017000663B1 (en) |
| CA (1) | CA2955402C (en) |
| EA (1) | EA033674B1 (en) |
| ES (1) | ES2709441T3 (en) |
| MX (2) | MX376447B (en) |
| PL (1) | PL3169769T3 (en) |
| RS (1) | RS58339B1 (en) |
| SI (1) | SI3169769T1 (en) |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN110144314A (en) * | 2019-05-30 | 2019-08-20 | 广东子辉生态环境科技有限公司 | A large-scale production method of micro-ecological flora for repairing black and odorous water bodies |
| EP3950252A1 (en) * | 2020-08-05 | 2022-02-09 | RubberSubstitute4.0 SA | Process for devulcanisation of rubber particles |
| CN117799084A (en) * | 2023-12-29 | 2024-04-02 | 德昌金锋橡胶有限公司 | A kind of process method for producing butyl recycled rubber |
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| EP3797799B1 (en) | 2019-09-27 | 2026-04-15 | Electronic Systems S.p.A. | Apparatus and method for de-vulcanisation of rubber |
| EP3797887B1 (en) * | 2019-09-27 | 2024-07-03 | Electronic Systems S.p.A. | Apparatus and method for removing rubber |
| CN110606782A (en) * | 2019-09-30 | 2019-12-24 | 广东森度生态农业科技有限公司 | Farmland soil water-retaining organic fertilizer and preparation method thereof |
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| US12103985B2 (en) | 2020-12-08 | 2024-10-01 | Arizona Board Of Regents On Behalf Of Arizona State University | Microbial desulfurization and surface activation of rubber |
| CN112779191B (en) * | 2021-02-04 | 2022-11-15 | 中国科学院过程工程研究所 | Breeding method and application of high-sulfur-oxidizing-performance desulfurization strain |
| CN116854990A (en) * | 2023-06-28 | 2023-10-10 | 元谋金蓬环保科技有限公司 | A kind of waste tire recycled rubber processing technology |
| CN121114115B (en) * | 2025-09-01 | 2026-07-17 | 中策橡胶集团股份有限公司 | Method, system and program product for rapidly detecting inorganic components of reclaimed rubber based on X-ray photoelectron spectroscopy |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5115983A (en) | 1990-07-07 | 1992-05-26 | D & R Recyclers, Inc. | Process for recycling vehicle tires |
| EP0493732A1 (en) | 1990-12-22 | 1992-07-08 | HÖLZEMANN METALLVERARBEITUNG GmbH | Process for processing of old rubber |
| US5597851A (en) | 1995-09-14 | 1997-01-28 | Battelle Memorial Institute | Method for the addition of vulcanized waste rubber to virgin rubber products |
| DE19728036A1 (en) | 1997-07-01 | 1999-01-07 | Hoelzemann System Und Umweltte | Surface activation and modification of sulphur-vulcanised rubber particles |
| EP1620498A1 (en) | 2003-04-01 | 2006-02-01 | Cristallo Holdings Inc. | Process for surface activation and/or devulcanisation of sulphur-vulcanised rubber particles |
Family Cites Families (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6407144B1 (en) * | 2000-04-04 | 2002-06-18 | Westinghouse Savannah River Company, Llc | Combination biological and microwave treatments of used rubber products |
| US6479558B1 (en) * | 2000-04-04 | 2002-11-12 | Westinghouse Savannah River Company | Microbial processing of used rubber |
| US7851177B2 (en) * | 2006-07-31 | 2010-12-14 | Biotechnologias Del Agua Ltda | Method for detecting presence of acidophilic microorganisms in bioleaching solution |
| CN101289549B (en) * | 2007-04-20 | 2011-02-16 | 北京化工大学 | Biological desulphurization process for waste and old rubber |
| CA2726423A1 (en) * | 2008-04-24 | 2009-10-29 | Swissjet Technology Sa | Process for the continuous cycle recycling of materials contained in products coupled to other materials by disintegration through water jets at high/ultrahigh pressure and products obtained in this way |
| IT1390993B1 (en) * | 2008-08-29 | 2011-10-27 | Verri | TIRES RECYCLING SYSTEM |
| IL209633A (en) * | 2010-11-29 | 2014-04-30 | Moshe Rakhman | Olefinic thermoplastic elastomer composition and process for producing the same |
| CN103923945B (en) * | 2014-04-16 | 2016-08-24 | 北京化工大学 | A kind of method utilizing microbial bacteria desulfurization regeneration scrap rubber |
-
2015
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- 2015-07-15 MX MX2017000693A patent/MX376447B/en active IP Right Grant
- 2015-07-15 ES ES15738346T patent/ES2709441T3/en active Active
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Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5115983A (en) | 1990-07-07 | 1992-05-26 | D & R Recyclers, Inc. | Process for recycling vehicle tires |
| EP0493732A1 (en) | 1990-12-22 | 1992-07-08 | HÖLZEMANN METALLVERARBEITUNG GmbH | Process for processing of old rubber |
| US5597851A (en) | 1995-09-14 | 1997-01-28 | Battelle Memorial Institute | Method for the addition of vulcanized waste rubber to virgin rubber products |
| DE19728036A1 (en) | 1997-07-01 | 1999-01-07 | Hoelzemann System Und Umweltte | Surface activation and modification of sulphur-vulcanised rubber particles |
| EP1620498A1 (en) | 2003-04-01 | 2006-02-01 | Cristallo Holdings Inc. | Process for surface activation and/or devulcanisation of sulphur-vulcanised rubber particles |
Non-Patent Citations (4)
| Title |
|---|
| ROMINE A. ROMINE ET AL.: "Rubbercycle: a bioprocess for surface modification of waste tyre rubber", POLYMER DEGRADATION AND STABILITY, vol. 59, 1998, pages 353 - 358 |
| ROMINE R A ET AL: "Rubbercycle: a bioprocess for surface modification of waste tyre rubber", POLYMER DEGRADATION AND STABILITY, BARKING, GB, vol. 59, no. 1-3, 3 January 1998 (1998-01-03), pages 353 - 358, XP027153179, ISSN: 0141-3910, [retrieved on 19980103] * |
| YUANHU LI ET AL.: "Microbial desulfurization of ground tire rubber by Thiobacillus ferrooxidans", POLYMER DEGRADATION AND STABILITY, vol. 96, no. 9, 2011, pages 1662 - 1668 |
| YUANHU LI ET AL: "Microbial desulfurization of ground tire rubber by", POLYMER DEGRADATION AND STABILITY, BARKING, GB, vol. 96, no. 9, 22 June 2011 (2011-06-22), pages 1662 - 1668, XP028249913, ISSN: 0141-3910, [retrieved on 20110628], DOI: 10.1016/J.POLYMDEGRADSTAB.2011.06.011 * |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110144314A (en) * | 2019-05-30 | 2019-08-20 | 广东子辉生态环境科技有限公司 | A large-scale production method of micro-ecological flora for repairing black and odorous water bodies |
| EP3950252A1 (en) * | 2020-08-05 | 2022-02-09 | RubberSubstitute4.0 SA | Process for devulcanisation of rubber particles |
| WO2022029193A1 (en) | 2020-08-05 | 2022-02-10 | Rubbersubstitute4.0 Sa | Method for devulcanization of rubber particles |
| CN117799084A (en) * | 2023-12-29 | 2024-04-02 | 德昌金锋橡胶有限公司 | A kind of process method for producing butyl recycled rubber |
Also Published As
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| CA2955402A1 (en) | 2016-01-21 |
| JP6825918B2 (en) | 2021-02-03 |
| BR112017000663A2 (en) | 2017-03-21 |
| EP3438244B1 (en) | 2023-06-07 |
| ES2709441T3 (en) | 2019-04-16 |
| CN107108951A (en) | 2017-08-29 |
| EA201790083A1 (en) | 2017-06-30 |
| US20210380933A1 (en) | 2021-12-09 |
| CA2955402C (en) | 2023-02-28 |
| KR102125115B1 (en) | 2020-06-22 |
| CN107108951B (en) | 2020-07-14 |
| MX2017000693A (en) | 2017-05-01 |
| TW201623389A (en) | 2016-07-01 |
| MX2020008008A (en) | 2020-09-10 |
| EA033674B1 (en) | 2019-11-14 |
| AU2015289182A1 (en) | 2017-02-09 |
| EP3169769B1 (en) | 2018-10-31 |
| EP3438244A1 (en) | 2019-02-06 |
| SI3169769T1 (en) | 2019-04-30 |
| PL3169769T3 (en) | 2019-05-31 |
| KR20170023183A (en) | 2017-03-02 |
| US11124759B2 (en) | 2021-09-21 |
| US20170211158A1 (en) | 2017-07-27 |
| BR112017000663B1 (en) | 2018-01-30 |
| JP2017527263A (en) | 2017-09-21 |
| EP3169769A1 (en) | 2017-05-24 |
| MX376447B (en) | 2025-03-07 |
| TWI663193B (en) | 2019-06-21 |
| RS58339B1 (en) | 2019-03-29 |
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