ES2293864A1 - Method for fungal biodegradation of shredded tires, involves using fungus and crushed tire is washed to eliminate interfering contamination - Google Patents
Method for fungal biodegradation of shredded tires, involves using fungus and crushed tire is washed to eliminate interfering contamination Download PDFInfo
- Publication number
- ES2293864A1 ES2293864A1 ES200703236A ES200703236A ES2293864A1 ES 2293864 A1 ES2293864 A1 ES 2293864A1 ES 200703236 A ES200703236 A ES 200703236A ES 200703236 A ES200703236 A ES 200703236A ES 2293864 A1 ES2293864 A1 ES 2293864A1
- Authority
- ES
- Spain
- Prior art keywords
- fungus
- crushing
- biodegradation
- tires
- rubber
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- 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
-
- 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
- C12N1/14—Fungi; Culture media therefor
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Genetics & Genomics (AREA)
- Wood Science & Technology (AREA)
- Medicinal Chemistry (AREA)
- Biotechnology (AREA)
- Zoology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Biomedical Technology (AREA)
- Virology (AREA)
- Tropical Medicine & Parasitology (AREA)
- General Engineering & Computer Science (AREA)
- Mycology (AREA)
- Botany (AREA)
- Sustainable Development (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Polymers & Plastics (AREA)
- Processing Of Solid Wastes (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
Description
Procedimiento de biodegradación fúngica de triturado de neumáticos.Fungal biodegradation procedure of Tire crushing
Industria del neumático, Gestión de neumáticos usados, Degradación de neumáticos usados.Tire industry, Tire management used, Degradation of used tires.
Durante los últimos años se han venido desarrollando procedimientos de biorremediación consistentes en la utilización de microorganismos para la recuperación de ambientes contaminados. Los esfuerzos en este campo han estado principalmente encaminados a la restauración de suelos contaminados con productos químicos tóxicos o peligrosos usando microorganismos; de esta forma se ha ido implantando el concepto de biorremediación. Adicionalmente, se han desarrollado en los últimos tiempos procesos de biodegradación aplicados a materiales contaminantes con vistas al posterior aprovechamiento y reutilización de sus componentes, siendo este el objeto del procedimiento que cubre la presente patente.In recent years they have come developing bioremediation procedures consisting of use of microorganisms for the recovery of environments contaminated Efforts in this field have been mainly aimed at the restoration of soils contaminated with products toxic or dangerous chemicals using microorganisms; thus The concept of bioremediation has been implemented. Additionally, processes have been developed in recent times of biodegradation applied to polluting materials with a view to subsequent use and reuse of its components, this being the object of the procedure that covers this patent.
El estudio de la biodegradación del caucho también se viene realizando desde hace años. La mayoría de los trabajos son de investigación básica y suponen fundamentalmente la participación de bacterias, aisladas principalmente de suelos, fuentes termales y restos de neumáticos en descomposición. Los actinomicetos han sido considerados las bacterias más importantes en la degradación de productos de caucho natural y vulcanizado, especialmente Nocardia. También se ha descrito, aunque en menor medida, el uso de hongos de podredumbre de la madera y sus enzimas para la descomposición de caucho vulcanizado.The study of the biodegradation of rubber has also been carried out for years. The majority of the works are of basic research and essentially involve the participation of bacteria, mainly isolated from soils, hot springs and the remains of decomposing tires. Actinomycetes have been considered the most important bacteria in the degradation of natural and vulcanized rubber products, especially Nocardia . It has also been described, although to a lesser extent, the use of wood rot fungi and their enzymes for the decomposition of vulcanized rubber.
El proceso de vulcanización sufrido por el caucho natural en los neumáticos y otros productos da cuenta de sus deseables propiedades mecánicas y térmicas, pero es al mismo tiempo responsable de que su reutilización sea compleja. Mediante este proceso se forman puentes disulfuro entre las cadenas de los polímeros, tanto de cauchos naturales como sintéticos. Se han descrito diversos procesos de desvulcanización química, física y microbiana. Asimismo se han documentado procesos de degradación que suponen únicamente la rotura de las cadenas poliméricas.The vulcanization process suffered by the natural rubber in tires and other products realizes their desirable mechanical and thermal properties, but it is at the same time responsible for its reuse is complex. Through this process disulfide bridges are formed between the chains of the polymers, both natural and synthetic rubbers. They have described various chemical, physical and chemical devulcanization processes microbial Also, degradation processes have been documented that they involve only the breakage of the polymer chains.
Como ya se ha dicho, hasta el momento los tratamientos microbiológicos de vulcanizados usados suponen principalmente la utilización de bacterias, lo cual aparece reflejado en varios documentos de patente. Por ejemplo, la patente japonesa JP2004313031 se refiere a la desulfuración de caucho vulcanizado triturado (caucho natural, o cauchos de butadieno) mediante bacilos Gram-positivos aislados del suelo.As already said, so far the Vulcanized microbiological treatments used mean mainly the use of bacteria, which appears reflected in several patent documents. For example, the patent Japanese JP2004313031 refers to the desulfurization of rubber crushed vulcanized (natural rubber, or butadiene rubbers) by Gram-positive bacilli isolated from ground.
En la patente americana US6479558, se utilizan bacterias aisladas de fuentes termales que contienen azufre, para la desvulcanización de caucho, de forma que mejore su aptitud para ser reciclado. Según WO01/74933, dicho biotratamiento puede completarse por un tratamiento con microondas.In US patent US6479558, they are used bacteria isolated from sulfur-containing hot springs, for rubber devulcanization, so as to improve your ability to be recycling. According to WO01 / 74933, said biotreatment can be completed for a microwave treatment.
La patente alemana DE4220623 plantea la desvulcanización de triturado de neumáticos usados con bacterias como Thiobacillus oxidans, Thiobacillus ferrooxidans y similares. En la patente española ES2086468 se emplean Thiobacillus ferrooxidans, Thiobacillus thiooxidans y/o Thiobacillus thioparis.German patent DE4220623 raises the devulcanization of crushed tires used with bacteria such as Thiobacillus oxidans, Thiobacillus ferrooxidans and the like. In Spanish patent ES2086468, Thiobacillus ferrooxidans, Thiobacillus thiooxidans and / or Thiobacillus thioparis are used .
La patente internacional WO2004/087799 divulga la activación superficial y/o desvulcanización superficial de partículas de caucho, por la acción de bacterias mesófilas o enzimas derivadas de las mismas. Se trata de bacterias que utilizan y/o reducen azufre, en concreto Desulfuromonas thiophila, Desulfuromonas palmitatis, Sulfurospirillum deleyianum o Desulfuromonas acetoxidans. US5597851 se refiere a la utilización de microbios tiófilos o enzimas procedentes de los mismos, para la desvulcanización superficial de caucho. Las bacterias se seleccionan entre Thiobacillus ferrooxidans, Thiobacillus thiooxidans, Rhodococcus rhodochrous y Sulfolobus acidocaldarius.The international patent WO2004 / 087799 discloses the surface activation and / or surface devulcanization of rubber particles, by the action of mesophilic bacteria or enzymes derived therefrom. These are bacteria that use and / or reduce sulfur, namely Desulfuromonas thiophila, Desulfuromonas palmitatis, Sulfurospirillum deleyianum or Desulfuromonas acetoxidans . US5597851 refers to the use of thiophilic microbes or enzymes derived therefrom, for the surface devulcanization of rubber. Bacteria are selected from Thiobacillus ferrooxidans, Thiobacillus thiooxidans, Rhodococcus rhodochrous and Sulfolobus acidocaldarius .
En el documento DE19728036 se emplea Thiobacillus ferrooxidans, Thiobacillus thiooxidans, Thiobacillus thioparus, Thiobacillus novellus, Sulfolobus acidocaldarius, Sulfolobus brierley, Acidanus acidaus, Rhodococcus rhodochrous o Pseudomonas putida para la activación y modificación de la superficie de partículas de caucho vulcanizado.In DE19728036, Thiobacillus ferrooxidans, Thiobacillus thiooxidans, Thiobacillus thioparus, Thiobacillus novellus, Sulfolobus acidocaldarius, Sulfolobus brierley, Acidanus acidaus, Rhodococcus rhodochrous or Pseudomonas vulcanized surface area and rubber modulation.
En la patente JP2003250526 se propone una nueva bacteria (Enterobacter cloacae MOE-1) para la descomposición de caucho natural o estireno-butadieno. En JP1096230 se emplea Xanthomonas NR-35Y (FERM 9640).In JP2003250526 a new bacterium ( Enterobacter cloacae MOE-1) is proposed for the decomposition of natural rubber or styrene-butadiene. In JP1096230 Xanthomonas NR-35Y (FERM 9640) is used.
En JP2004131643 se plantea la descomposición de productos que contienen caucho natural, como neumáticos usados, mediante actinomicetos del género Nocardia. El documento JP2006182952 se refiere a la obtención de polvo de caucho apto para ser reutilizado, que se obtiene por tratamiento de la superficie de caucho triturado con Nocardia actinomyces cepa BS-HA1 (FERM P-19378). En JP2006180822 también se describe dicha cepa. En JP2006180794 se describe la cepa Nocardia BS-TAI (FERM P-19379) y su utilidad para degradar caucho. De acuerdo con JP11060793, la biodegradación de caucho duro, como el procedente de neumáticos, se lleva a cabo con actinomicetos del género Nocardia, preferentemente de la cepa Rd-Cm o una variante, específicamente depositada como FERM P-16338. En US5854058 también se emplea el género Nocardia, cepa NR-35A. Esa misma cepa de Nocardia y Rhodococcus NR-26S, se utilizan en JP61085193 y JP60072934 para degradar polímeros de isopreno, naturales o sintéticos. Nocardia (NR-35A) y Rhodococcus también se utilizan en JP2076575 para la descomposición de caucho. JP54055778 propone el uso de Pseudomonas cepa AT-S-1 y Nocardia cepa AT-S-3.In JP2004131643 the decomposition of products containing natural rubber, such as used tires, is proposed by actinomycetes of the genus Nocardia . JP2006182952 refers to obtaining rubber powder suitable for reuse, which is obtained by treating the surface of rubber crushed with Nocardia actinomyces strain BS-HA1 (FERM P-19378). This strain is also described in JP2006180822. JP2006180794 describes the Nocardia strain BS-TAI (FERM P-19379) and its usefulness for degrading rubber. According to JP11060793, the biodegradation of hard rubber, such as that derived from tires, is carried out with actinomycetes of the genus Nocardia , preferably of the strain Rd-Cm or a variant, specifically deposited as FERM P-16338. In US5854058 the genus Nocardia , strain NR-35A is also used. That same strain of Nocardia and Rhodococcus NR-26S, are used in JP61085193 and JP60072934 to degrade isoprene polymers, natural or synthetic. Nocardia (NR-35A) and Rhodococcus are also used in JP2076575 for rubber decomposition. JP54055778 proposes the use of Pseudomonas strain AT-S-1 and Nocardia strain AT-S-3.
La solicitud europea EP1454942 emplea una cepa WU-YSO5 de Pseudonocardiaceae para producir rugosidades en la superficie de caucho pulverizado. Esta bacteria también se emplea en JP2003231118. Rhodococcus rhodochrous ATCC 53968 se utiliza en EPO441462 para la ruptura de enlaces carbono-azufre, por ejemplo en el reciclado de caucho. Esa bacteria y/o Bacillus sphaericus ATCC 53969 se pueden utilizar según EP0562313 y US5358869, con el mismo fin.European application EP1454942 employs a WU-YSO5 strain of Pseudonocardiaceae to produce surface roughness of powdered rubber. This bacterium is also used in JP2003231118. Rhodococcus rhodochrous ATCC 53968 is used in EPO441462 for the rupture of carbon-sulfur bonds, for example in rubber recycling. That bacterium and / or Bacillus sphaericus ATCC 53969 can be used according to EP0562313 and US5358869, for the same purpose.
La solicitud PCT WO2004/076492 propone utilizar actinomicetos, p. ej. de los géneros Corynebacterium, Rhodococcus, Nocardia, Gordonia, Tsukamurella, Dietzia y Mycobacterium. En especial, se utiliza Gordonia desulfuricans SG213E para biotratamiento de caucho natural o sintético.PCT application WO2004 / 076492 proposes to use actinomycetes, e.g. ex. of the genera Corynebacterium, Rhodococcus, Nocardia, Gordonia, Tsukamurella, Dietzia and Mycobacterium . In particular, Gordonia desulfuricans SG213E is used for biotreatment of natural or synthetic rubber.
Las patentes que se refieren a la utilización de hongos para el tratamiento de cauchos, naturales o vulcanizados, son mucho más escasas. Sólo JP2004099738 propone tratar caucho vulcanizado natural o sintético con hongos de la podredumbre de la madera, como p. ej. Ceriporiopsis subvermispora (FP 90081) y Dichomitus squalens (CBS 482.84). Por otra parte, JP2006152237 y JP2005232347 utilizan enzimas aisladas de hongos de la podredumbre de la madera, para la descomposición de caucho vulcanizado.Patents that refer to the use of fungi for the treatment of rubbers, natural or vulcanized, are much scarcer. Only JP2004099738 proposes to treat natural or synthetic vulcanized rubber with wood rot fungi, such as p. ex. Ceriporiopsis subvermispora (FP 90081) and Dichomitus squalens (CBS 482.84). On the other hand, JP2006152237 and JP2005232347 use enzymes isolated from fungi of wood rot, for the decomposition of vulcanized rubber.
Con el procedimiento que se presenta en esta patente se consigue la biodegradación de un triturado heterogéneo de neumáticos comerciales usados por medio del hongo Paecilomyces lilacinus IMI 117109.With the procedure presented in this patent, the biodegradation of a heterogeneous crushing of commercial tires used by means of the Paecilomyces lilacinus IMI 117109 fungus is achieved.
Para llevar a cabo la degradación citada anteriormente del triturado de neumático usado se ha ideado un procedimiento de biodegradación en el cual se cultiva el hongo en un medio líquido de sales minerales en el que el material triturado constituye la única fuente de carbono para el microorganismo.To carry out the aforementioned degradation previously of the crushing of used tire has been devised a biodegradation procedure in which the fungus is grown in a liquid medium of mineral salts in which the crushed material It is the only source of carbon for the microorganism.
Previamente a la incubación del triturado de neumático con el hongo, se lleva a cabo un lavado del triturado en unas determinadas condiciones de relación peso de triturado/volumen de agua estéril utilizada, temperatura, agitación y tiempo. Este lavado permite la eliminación de restos orgánicos y microorganismos contaminantes que pudieran interferir o desplazar la reacción de biodegradación.Prior to the crushing incubation of pneumatic with the fungus, a crushing wash is carried out in certain conditions of crushing weight / volume ratio of sterile water used, temperature, agitation and time. This washing allows the elimination of organic remains and microorganisms contaminants that could interfere or displace the reaction of biodegradation
A continuación se realizan cultivos del hongo en un medio líquido de sales minerales y sin fuentes de carbono. De esta manera se asegura que los únicos nutrientes que pueden ser metabolizados por el hongo son los compuestos poliméricos que forman mayoritariamente el triturado de neumático.Cultures of the fungus are then carried out in a liquid medium of mineral salts and without carbon sources. From This way ensures that the only nutrients that can be metabolized by the fungus are the polymeric compounds that form mostly tire crushing.
El cultivo del hongo en el triturado de neumático con el medio de sales minerales se realiza en dos fases: en la primera se realiza un cultivo en medio líquido, con un exceso de medio y agitación. Esta fase es necesaria para la activación y correcta distribución del hongo en el triturado. En la segunda fase se retira el exceso de medio líquido, quedando un cultivo sólido-húmedo estático, en el que continúa desarrollándose el hongo sobre el triturado.Cultivation of the fungus in the crushing of pneumatic with the mineral salts medium is carried out in two phases: in the first one a culture is carried out in liquid medium, with an excess of medium and agitation. This phase is necessary for activation and correct distribution of the fungus in the crushed. In the second phase excess liquid medium is removed, leaving a culture solid-wet static, in which it continues developing the fungus on the crushed.
El desarrollo fúngico es una señal inequívoca del proceso de biodegradación que está teniendo lugar en el triturado de neumático.Fungal development is an unequivocal signal of the biodegradation process that is taking place in the crushed tire
El procedimiento descrito también puede ser eventualmente aplicado a otros microorganismos, como otros hongos e incluso bacterias siempre que posean las capacidades metabólicas necesarias para la degradación del triturado de neumático, y adaptando las condiciones del proceso a la fisiología particular de los microorganismos a considerar.The procedure described can also be possibly applied to other microorganisms, such as other fungi and even bacteria as long as they possess metabolic abilities necessary for tire crushing degradation, and adapting the process conditions to the particular physiology of The microorganisms to consider.
El triturado de neumático utilizado para la realización de este procedimiento es de granulometria 3 < x < 4 mm, procedente de diversos neumáticos usados de composición comercial, todos ellos basados en una matriz polimérica de caucho natural o sintético entrecruzada por puentes disulfuro en su vulcanización.The tire crushing used for the Performing this procedure is granulometry 3 <x < 4 mm, from various used tires of composition commercial, all based on a polymer matrix of rubber natural or synthetic crosslinked by disulfide bridges in its vulcanization.
La primera parte del procedimiento consiste en la preparación del triturado de neumático que se usará corno sustrato de la biodegradación. Se lleva a cabo un lavado del triturado en las siguientes condiciones: relación peso de triturado/volumen de agua estéril utilizada de 0,25 (50 g de triturado por cada 200 mL de agua) en matraces Erlenmeyer de 250 mL. Estos se incuban a 50ºC y 140 rpm durante 24 h en un agitador orbital (Lab-Line® Orbit Environ-Shaker. Lab-Line Instruments, Inc., Melrose Park, ILL, USA). Se lleva a cabo este proceso dos veces.The first part of the procedure consists of tire crushing preparation to be used as biodegradation substrate. A washing of the crushed under the following conditions: weight ratio of crushed / used volume of sterile water of 0.25 (50 g of crushed for every 200 mL of water) in 250 Erlenmeyer flasks mL These are incubated at 50 ° C and 140 rpm for 24 hours on a shaker orbital (Lab-Line® Orbit Environ-Shaker Lab-Line Instruments, Inc., Melrose Park, ILL, USA). This is done process twice.
Por medio de este procedimiento se realizan cultivos en matraces Erlenmeyer de 250 mL. El medio de cultivo utilizado es MSB (Mineral Salts Broth; Zaborski y cols., 2006, Polimery, 51 (7-8): 534-538). Como inóculo se utilizan 6 tacos extraídos con Tranfertubes® (Spectrum Laboratories, Inc., Rancho Domínguez, CA, USA) de una placa Petri con el hongo crecido durante 4 semanas. La relación peso de triturado/volumen de medio utilizada es de 0,4 (10 g de triturado de neumático por cada 25 mL de medio).Through this procedure they are performed 250 mL Erlenmeyer flask cultures. Culture medium used is MSB (Mineral Salts Broth; Zaborski et al., 2006, Polimery, 51 (7-8): 534-538). How inoculum 6 tacos extracted with Tranfertubes® (Spectrum) are used Laboratories, Inc., Rancho Dominguez, CA, USA) of a Petri dish with the fungus grown for 4 weeks. The weight ratio of Crushed / volume of medium used is 0.4 (10 g of crushed pneumatic per 25 mL of medium).
\newpage\ newpage
Los matraces se incuban durante una semana en un agitador orbital a 25ºC y con una agitación de 100 rpm. Una vez transcurrido este tiempo, se retira el exceso de medio y, en condiciones estériles, se coloca el triturado húmedo en placas Petri. Estas placas se sellan con cinta de parafina (Parafilm®. Pechiney Plastic Packaging, Menasha, WI, USA) y se incuban a 25ºC durante 1 semana. Una vez transcurrido este tiempo se observa visualmente un claro desarrollo del micelio del hongo sobre el triturado de neumático húmedo, en el que son claramente apreciables, por microscopía electrónica de barrido a baja temperatura, los surcos sobre la superficie del material y las galerías en su interior, creados por las hifas del hongo en su crecimiento.The flasks are incubated for a week in a orbital shaker at 25 ° C and with a stirring of 100 rpm. One time after this time, the excess medium is removed and, in sterile conditions, wet crushing is placed on plates Petri These plates are sealed with paraffin tape (Parafilm®. Pechiney Plastic Packaging, Menasha, WI, USA) and incubate at 25 ° C for 1 week After this time is observed visually a clear development of the mycelium of the fungus on the crushed wet tire, in which they are clearly appreciable, by scanning electron microscopy at low temperature, the grooves on the surface of the material and the galleries inside, created by the hyphae of the fungus in its increase.
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
ES200703236A ES2293864B2 (en) | 2007-12-05 | 2007-12-05 | PROCEDURE OF FUNGICAL BIODEGRADATION OF CRUSHING OF TIRES. |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
ES200703236A ES2293864B2 (en) | 2007-12-05 | 2007-12-05 | PROCEDURE OF FUNGICAL BIODEGRADATION OF CRUSHING OF TIRES. |
Publications (2)
Publication Number | Publication Date |
---|---|
ES2293864A1 true ES2293864A1 (en) | 2008-03-16 |
ES2293864B2 ES2293864B2 (en) | 2009-04-01 |
Family
ID=39166536
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
ES200703236A Expired - Fee Related ES2293864B2 (en) | 2007-12-05 | 2007-12-05 | PROCEDURE OF FUNGICAL BIODEGRADATION OF CRUSHING OF TIRES. |
Country Status (1)
Country | Link |
---|---|
ES (1) | ES2293864B2 (en) |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06322263A (en) * | 1993-05-14 | 1994-11-22 | Kuraray Co Ltd | Biodegradable polymer composition and molded article |
JP2004099738A (en) * | 2002-09-09 | 2004-04-02 | Sumitomo Rubber Ind Ltd | Decomposition treatment method for vulcanized rubber composition using wood putrefactive bacteria |
EP1454942A1 (en) * | 2001-12-04 | 2004-09-08 | Bridgestone Corporation | Powdery rubber having unevened surface and rubber compositions and tires using the same |
-
2007
- 2007-12-05 ES ES200703236A patent/ES2293864B2/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06322263A (en) * | 1993-05-14 | 1994-11-22 | Kuraray Co Ltd | Biodegradable polymer composition and molded article |
EP1454942A1 (en) * | 2001-12-04 | 2004-09-08 | Bridgestone Corporation | Powdery rubber having unevened surface and rubber compositions and tires using the same |
JP2004099738A (en) * | 2002-09-09 | 2004-04-02 | Sumitomo Rubber Ind Ltd | Decomposition treatment method for vulcanized rubber composition using wood putrefactive bacteria |
Non-Patent Citations (10)
Title |
---|
[en línea] [Recuperado el 25.02.2008] Recuperado de: EPO EPODOC Database. & JP 06322263 A (KURAKAY CO.) 22.11.1994, (resumen) * |
[en línea] [Recuperado el 25.02.2008] Recuperado de: EPO WPI Database & JP 2004099738 A (SUMITOMO RUBBER IND.) 02.04.2004 (resumen) * |
Biodeteriogens. CABI Strain Microbial properties. CABI Bioscience. 24.11.2005 [en línea] [Recuperado el 25.02.2008] Recuperado de internet: <http://www.cabi-bioscience.org/microbialproperties.asp> * |
BREDBERG, K. et al. Microbial detoxification of waste rubber material by wood-rotting fungi. Bioresource Technology. Julio, 2002. Vol. 83, Nº 3, páginas 221-224. ISSN 0960-8524. * |
LUGAUSKAS, A. et al. Physical and chemical aspects of long-term biodeterioration of some polymers and composites. Environmental Toxicology. Vol. 19, Nº 4. Agosto, 2004 (resumen) [en línea] [Recuperado el 25.02.2008] Recuperado de: EPO BIOSIS Database. * |
ROY, R.V. et al. Comparative studies on rubber biodegradation through solid-state and submerged fermentation. Process Biochemistry. 2006. Vol. 41, Nº 1, páginas 181-186. * |
ROY, R.V. et al. Comparative studies on rubber biodegradation through solid-state and submerged fermentation. Process Biochemistry. 2006. Vol. 41, Nº 1, páginas 181-186. \\ Y 3 * |
SATO, S. et al. Microbial Scission of Sulfide Linkages in Vulcanized Natural Rubber by a White Rot Basidiomycete, Ceriporiopsis subvermispora. Biomacromolecules. Marzo-Abril 2004. Vol. 5, Nº 2, páginas 511-515. ISSN 1525-7797. * |
WALLSTRÖM, S. et al. Development and comparison of test methods for evaluating formation of biofilms on silicones. Polymer Degradation and Stability.2002. Vol. 78, páginas 257-262. * |
WALLSTRÖM, S. et al. Development and comparison of test methods for evaluating formation of biofilms on silicones. Polymer Degradation and Stability.2002. Vol. 78, páginas 257-262. \\ A 3,4 * |
Also Published As
Publication number | Publication date |
---|---|
ES2293864B2 (en) | 2009-04-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Maroof et al. | Identification and characterization of low density polyethylene-degrading bacteria isolated from soils of waste disposal sites | |
Soleimani et al. | A survey of intact low-density polyethylene film biodegradation by terrestrial Actinobacterial species | |
Bardají et al. | Isolation of a polyethylene degrading Paenibacillus sp. from a landfill in Brazil | |
Mukherjee et al. | Bioremediation and reclamation of soil contaminated with petroleum oil hydrocarbons by exogenously seeded bacterial consortium: a pilot-scale study | |
Eskandari et al. | Bioremediation of polycyclic aromatic hydrocarbons by Bacillus Licheniformis ATHE9 and Bacillus Mojavensis ATHE13 as newly strains isolated from oil-contaminated soil | |
Bergauer et al. | Biodegradation of phenol and phenol-related compounds by psychrophilic and cold-tolerant alpine yeasts | |
Heisey et al. | Isolation of microorganisms able to metabolize purified natural rubber | |
Ghavipanjeh et al. | Devulcanization of ground tires by different strains of bacteria: optimization of culture condition by taguchi method | |
Sahoo et al. | Isolation and characterization of a lindane degrading bacteria Paracoccus sp. NITDBR1 and evaluation of its plant growth promoting traits | |
Ma et al. | Bioaugmentation of soil contaminated with high-level crude oil through inoculation with mixed cultures including Acremonium sp. | |
Zhou et al. | A novel strategy for enhancing bioremediation of polychlorinated biphenyl-contaminated soil with resuscitation promoting factor and resuscitated strain | |
Tatangelo et al. | Biological devulcanization of ground natural rubber by Gordonia desulfuricans DSM 44462 T strain | |
Sato et al. | Microbial scission of sulfide linkages in vulcanized natural rubber by a white rot basidiomycete, ceriporiopsis s ubvermispora | |
Heidari et al. | Bisphenol A degradation by Ralstonia eutropha in the absence and presence of phenol | |
CN111902434B (en) | Microorganisms for waste treatment | |
CN108130288A (en) | The application of Rhodococcus ruber and its degradable organic pollutant | |
Puškárová et al. | Diversity and PAH growth abilities of bacterial strains isolated from a contaminated soil in Slovakia | |
Maroof et al. | Microbial degradation of low density polyethylene by Exiguobacterium sp. strain LM-IK2 isolated from plastic dumped soil | |
Ingavale et al. | Comparative biodegradation studies of LDPE and HDPE using Bacillus weihenstephanensis isolated from garbage soil | |
Bosco et al. | Biodegradation of natural rubber: microcosm study | |
Lao et al. | Degradation of scrap tyre by Bacillus sp.–Kinetic aspects of major environmental parameters and identification of potential growth substrates | |
Joseph et al. | Biodegradation of natural rubber by fungi and bacteria | |
US6503746B1 (en) | Biologically pure Paenibacillus validus bacterial strains that degrade polyaromatic hydrocarbons | |
ES2293864B2 (en) | PROCEDURE OF FUNGICAL BIODEGRADATION OF CRUSHING OF TIRES. | |
Srivastava et al. | Biodegradation of technical hexachlorocyclohexane by Cupriavidus malaysiensis |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
EC2A | Search report published |
Date of ref document: 20080316 Kind code of ref document: A1 |
|
FG2A | Definitive protection |
Ref document number: 2293864B2 Country of ref document: ES |
|
FA2A | Application withdrawn |
Effective date: 20091029 |
|
FD2A | Announcement of lapse in spain |
Effective date: 20211119 |