289results about How to "Promote biodegradation" patented technology

An isolated Bacillus amyloliquefaciens Ba-BPD1 having an Accession No. of DSM 21836 is provided. This novel strain has unique 16S ribosomal RNA sequenced as SEQ ID NO:1 and produces amylase, protease, cellulase and lipase, fibrinolytic enzyme to show their biodegradation capacities. Further, B. amyloliquefaciens Ba-BPD1 produces the antibiotic substances, such as iturin, fengycin and surfactin, and has antimicrobial capacity for inhibiting the fungal or bacterial growth. In conclusion, the novel strain of Bacillus amyloliquefaciens Ba-BPD1 and its products can be applied in agriculture, wastewater treatment, food industry and chemical industry.

The invention provides a progressive repair method for soil polluted by chlorinated organic compounds. The repair method comprises the following steps: leaching the organic polluted soil by a water solution containing a bio-surfactant, and distributing most of persistent organic pollutants in the soil into a leaching solution; after finishing leaching, adding microbial degrading bacteria, and realizing the sustainable degradation of low-concentration organic compounds. The residual bio-surfactant cannot perform a negative function on the subsequent biodegradation of the organic pollutants, and can be used as a carbon source and be utilized by microorganisms. The bio-surfactant is used as a leaching agent, the organic pollutants are progressively degraded by a microorganism process, and the problems that the soil polluted by high-concentration chlorinated organic compounds is difficult to repair, traditional bio-surfactant produces residual toxicity, and the like are solved.

The invention relates to a dual-degradant additive for promoting photo oxidative degradation and biodegradation of a polymer, comprising the following ingredients: 30-50 wt% of resin used as a carrier, 26-40 wt% of composite photo oxidative degradation accelerating agent, 1-5 wt% of photo oxidative degradation induction period regulator, 1-5 wt% of carboxylic acid or its derivative, and 15-25 wt%of microcapsule composite material. The dual-degradant additive disclosed herein can be applied on various polymers. By using the dual-degradant additive to mix with the polymer according to a certain proportion to prepare a composite material, the composite material can be degraded through photo oxidative degradation and biodegradation, has effects of repairing soil and compost, and has effects of oxygen barrier and flame resistance in many applications.

A bowl-shaped container (10a) which is as a biodegradable molded article adheres a coating film (12) mainly made of biodegradable plastic and having at least hydrophobicity to the surface of the main body (11a) of the container mainly made of starch. The main body (11a) is molded through steam expansion of a slurry or dough molding material containing high-amylose starch and water, or a slurry or dough molding material containing starch, polyvinyl alcohol and water. For these reasons, it is possible to accomplish sufficient strength and at least sufficient water resistance, to exert a very excellent biodegradability and further to provide a biodegradable molded article having excellent moisture absorption strength mainly made of starch even if the biodegradable molded article has a complicated shape.

The invention discloses a sludge resource recovery method based on hydrothermal treatment of digested sludge. The method comprises the following steps: performing dehydration treatment on sludge so as to obtain dehydrated sludge with the solid content of 15-20%; mixing the dehydrated sludge and a press filtrate in which nitrogen and phosphorus are removed in a slurrying and tempering reactor, preheating, slurrying and tempering; pumping the sludge subjected to slurrying and tempering into an anaerobic digestion system so as to produce biogas; introducing the sludge subjected to anaerobic digestion into a pyrohydrolysis reactor for performing hydrothermal treatment, relieving pressure and cooling after pyrohydrolysis so as to obtain a mixed solution, and performing plate-frame pressure filtration dehydration so as to form high-dryness biogas residues; regulating the pH value of the press filtrate to 9-11, adding a magnesium salt to produce struvite so as to realize phosphorus recovery; regulating the pH value to 11-13, and performing ammonia stripping, thereby realizing nitrogen recovery; and refluxing the press filtrate in which nitrogen and phosphorus are removed back to the slurrying and tempering reactor, mixing with the dehydrated sludge, and performing cycle treatment. The method disclosed by the invention has the advantages that the sludge degradation rate and methane yield are effectively improved, and nitrogen and phosphorus resources are recovered.

The invention belongs to the field of workover operations, and particularly relates to a degradable temporary plugging agent for workover and a preparation method thereof. The degradable temporary plugging agent comprises the following components in parts by mass: 5-7% of acrylic acid, 15-21% of acrylamide, 5-15% of inorganic mineral soil, 0.002-0.005% of a polymerization inhibitor, 6-12% of a degradation promoter, 0.02-0.1% of a crosslinking agent, 0.6-1.0% of an initiator, 7-10% of corn flour and the balance of water. The degradable temporary plugging agent for workover disclosed by the invention has good degradation performance and does not need to add an additional degradation process; for high-water cut oil wells, water wells and the like, the degradable temporary plugging agent can be degraded by itself and resume operation and production only under the condition of a reservoir (under the condition of 90 DEG C, the 48-hour degradation rate can reach more than 90%).

The invention discloses an efficient treatment process for printing and dyeing waste water. In the invention, after printing and dyeing waste water is homogenated by a regulating tank and preaerated by a preaeration tank, the printing and dyeing waste water enters a primary precipitating tank to be precipitated; the precipitated waste water enters an oxygen deficiency or an aerobic membrane bioreactor to be treated, and chemical flocculants and biological microcarrier with an absorption function are thrown into an oxygen deficiency zone of the membrane bioreactor; waste water mixture liquid enters an aerobic zone from the oxygen deficiency zone, and is separated by a membrane assembly in the aerobic zone; clean water realizes standard discharge after being filtered by the membrane assembly, and biochemical or materialized mud with high concentration in the aerobic zone respectively returns to the oxygen deficiency zone and the preaeration tank; the biochemical or materialized mud returning to the oxygen deficiency zone is continuously recycled in the membrane bioreactor; and after the biochemical or materialized mud returning to the preaeration tank mixes with the homogenated printing and dyeing waste water for biochemical or materialized absorption and flocculation, the biochemical or materialized mud returning to the preaeration tank enters the primary precipitating tank to be precipitated, and the precipitated mud is discharged out of the system. The invention is not only applicable for the treatment of printing and dyeing waste water, and is also suitable for the treatment of other difficultly degraded waste water.

The invention discloses a sludge reflow-free device with a simultaneous nitrification and denitrification (SND) function. The device comprises a pool body; the sidewall of the pool body is provided with a main water inlet; the interior of the pool body is divided by a clapboard into a diversion area, an aeration area and a sludge precipitation area in sequence; the aeration area is internally provided with an overflow groove; the bottom of the aeration area is provided with microporous aeration devices distributed uniformly; and the sludge precipitation area is internally provided with a membrane element. The invention also discloses an operation control method of the device. By skillful arrangement of aeration pipes and combined use with a biological membrane, the power cost and the operating cost of sludge reflow are saved, and the purpose of reducing energy consumption is achieved. The biological environment to be achieved by the simultaneous nitrification and denitrification is adjusted indirectly through adjusting parameters such as active sludge concentration, sludge age, unit sludge load and the like; the operation is strong in human controllability, and the problem that the microbial metabolic environment in the SND technology is not easy to control is solved.

The invention relates to an agricultural waste-composting treatment method taking stream explosion method for pretreatment. The method comprises: proportioning materials in a C/N ratio of 20:1-30:1; determining the appropriate dosage of crops straw and livestock/poultry excrement; mixing the determined raw materials well; performing stream explosion pretreatment; adjusting water content to be between 50 and 60 percent; and performing composting treatment for 25 to 28 days to obtain organic fertilizer rich in organic substances and nutrients. By utilizing a stream explosion technique to treat agricultural waste, the method has the advantages of effectively improving the biological conversion rate of aerobic or anaerobic treatment and shortening treatment time, thereby achieving the aims of improving equipment utilization rate, reducing operation cost, solving the problem of environmental pollution and bringing social and economic benefits.

Systems and methods for co-enhancing contaminant degradation such as LNAPL and DNAPL degradation. Embodiments of the inventive technology may relate to assuring adequate amounts (e.g., concentrations) of certain substances (e.g., nitrogen, electron acceptor, bacteria, microbial substrate) so that degradation of LNAPL and DNAPL is enhanced as intended. Any of the inventive methods may involve the amendment of groundwater with one or more particular substance (uric acid, electron acceptors, microbial substrate, as but a few examples) in order to enhance DNAPL, and perhaps also, LNAPL degradation.

The invention discloses a lipopeptide-producing bacillus pumilus, and classification thereof is named to be Bacillus pumilus Y8A which is preserved by China Center for Type Culture Collection (CCTCC) in Wuhan University with the preservation number of CCTCCM 209108. The invention also discloses an application of the lipopeptide-producing bacillus pumilus in promoting the micro-biological degradation process of petroleum and/or cyhalothrin pesticide. Bacterial strain Y8A of the invention can produce lipopeptide biosurfactant with high efficiency and stability, thereby effectively promoting the micro-biological degradation process of petroleum and/or cyhalothrin pesticide degrading bacteria. Bacterial strain Y8A with the function of efficiently producing lipopeptide is expected to work as a new-generation bacteria and cosolvent for antibiotic production and, is widely used in agriculture, medicine, cosmetic and food industries, and can be used for restoration of pollutant environment together with other organic pollution degrading microbes. The bacterial strain is resistant to a plurality of antibiotics with easy fermentation course and convenient operation.

The invention relates to a composite porous scaffold and a preparation method thereof, in particular to a composite porous scaffold combining calcium sulfate and apatite compound and a preparation method thereof, and pertains to the technical field of medical apparatus and instruments. Composite sizing material combining calcium sulfate hemihydrate powder and crushed apatite compound is first prepared; calcium sulfate sizing material is evenly brushed on polyurethane foam to obtain a porous calcium sulfate ceramic scaffold after the steps of drying and high-temperature treatment. The obtained porous calcium sulfate ceramic scaffold is then immersed in the composite sizing material and then placed indoors for natural drying after the treatment of sizing hanging and finally heated and dried to obtain the composite porous scaffold combining calcium sulfate and apatite compound of the invention.