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31 results about "Phanerochaete sp." patented technology

Structure capable of being used for treating heavy metals in bottom mud dredging tail water and construction method thereof

The invention discloses a structure capable of being used for treating heavy metals in bottom mud dredging tail water. The structure comprises a settling pond and a reaction pool, wherein the reaction pool comprises an adjusting column and at least one absorption column. The adjusting column and the absorption columns use a grating cylinder mould as a frame, the adjusting column is filled with a solid particle filler and the absorption columns are filled with compounds consisting of Fe3O4-calcium alginate-phanerochaete chrysosporium microspheres. The adjusting column and the absorption columns are sequentially arranged along a water flow direction. A construction method of the structure comprises the following steps: constructing the settling pond and the reaction pool; digging more than two grooves in the reaction pool; placing the grating cylinder mould in a direction vertical to the water follow; filling the solid particle filler to the most upstream groove, filling compound biological absorption materials in the balance of grooves, and ensuring that the filler is higher than the water line of the reaction pool. The method disclosed by the invention has the advantages of low cost, simple preparation process, high absorption efficiency and the like, and can be used for treating heavy metal pollutants in the bottom mud dredging tail water.
Owner:HUNAN UNIV

Complex microbial inoculant for efficient degradation of straw and preparation method and application of complex microbial inoculant

The invention relates to the technical field of microorganisms, in particular to a complex microbial inoculant for efficient degradation of straw and a preparation method and application of the complex microbial inoculant. The complex microbial inoculant comprises a flora A, a flora B and a flora C; the flora A comprises aspergillus fumigatus, aspergillus versicolor, trichoderma harzianum, phanerochaete chrysosporium and auricularia polytricha; the flora B comprises bacillus subtilis, bacillus licheniformis and bacillus amyloliquefaciens; and the flora C comprises depubyomyces hansenii, pichia guilliermondii, bacillus subtilis, bacillus cereus and aneurinibacillus. The flora A is used for preparing a microbial agent I, the flora A and the flora B are used for preparing a microbial agent II, the flora A and the flora C are used for preparing a microbial agent III, and the flora A, the flora B and the flora C are used for preparing a microbial agent IV. According to the complex microbial inoculant, the flora A which is close to the environment and has a lignocellulose degradation function is preferably selected from the natural environment by a traditional microbiological method, and the flora B and the flora C are combined to achieve a synergistic effect, so that the straw degradation efficiency is effectively improved, and the complex microbial inoculant has important guiding significance on straw resource utilization.
Owner:SOUTHWEST JIAOTONG UNIV

Composite microbial preparation for degrading high-oil-content kitchen waste and preparation method and application thereof

InactiveCN113308409AGood synergyStrong oil degradation abilityBio-organic fraction processingFungiCellulosePhanerochaete sp.
The invention provides a preparation method of a composite microbial preparation for degrading high-oil-content kitchen waste. The composite microbial preparation comprises acinetobacter johnsonii, candida utilis, phanerochaete chrysosporium, bacillus subtilis and geobacillus stearothermophilus. The method comprises the following steps of S1, inoculating strains subjected to activation culture to a fermentation culture medium according to the mass percent of 5%, and performing fermentation culture, and S2, mixing the thalli cultured in the step S1 to prepare liquid mixed bacteria, mixing the liquid mixed bacteria with a solid adsorption carrier according to a mass ratio of 1: (1.5-2), and carrying out carrier adsorption and drying to obtain a composite microbial preparation. The liquid mixed bacteria comprise 30 to 40 percent of acinetobacter johnsonii, 10 to 20 percent of candida utilis, 10 to 15 percent of phanerochaete chrysosporium, 10 to 20 percent of bacillus subtilis and 10 to 20 percent of geobacillus stearothermophilus. Macromolecular compounds such as animal fat, vegetable fat and cellulose which are not easy to decompose in the kitchen waste can be efficiently and rapidly decomposed, and the degradation rate of protein and starch is maintained.
Owner:ANHUI QINGMING ENVIRONMENTAL PROTECTION TECH CO LTD

Structure capable of being used for treating heavy metals in bottom mud dredging tail water and construction method thereof

The invention discloses a structure that can be used for treating heavy metal pollutants in tail water of sediment dredging, including a sedimentation tank and a reaction tank, the reaction tank includes an adjustment column and at least one adsorption column, and the adjustment column and the adsorption column both adopt grids The mesh cage is used as a frame, and the regulating column is filled with solid particle filler, and the adsorption column is filled with a composite composed of Fe3O4-calcium alginate-Phanerochaete chrysosporium microspheres; and the regulating column and the adsorption column are arranged along the direction of water flow in sequence. The construction of the structure includes the following steps: build the sedimentation tank and the reaction tank, excavate more than two grooves in the reaction tank, and place the grid cage in each groove vertically to the direction of water flow; Fill the solid particle filler in the groove, and fill the composite bioabsorbent material in the remaining grooves, and ensure that the filler is higher than the water level line of the reaction tank. The invention has the advantages of low cost, simple preparation process, high adsorption efficiency, etc., and can be used for treating heavy metal pollutants in tail water of sediment dredging.
Owner:HUNAN UNIV

Photocatalytic biosorbent and its preparation method and application

The invention discloses a photocatalysis bio-adsorbent and a preparing method and application thereof. The photocatalysis bio-adsorbent comprises phanerochaete chrysosporium balls, graphite type C3N4 and calcium alginate, wherein graphite type C3N4 is wrapped in hyphae of the phanerochaete chrysosporium balls through calcium alginate. The preparing method comprises the steps of adding graphite type C3N4 to sodium alga acid solution for ultrasonic dispersion, then adding phanerochaete chrysosporium spore suspension, conducting uniform mixing, adding obtained mixed solution to calcium chloride solution dropwise for hardening, and conducting shake cultivation on embedding spheres obtained after hardening so as to obtain the photocatalysis bio-adsorbent finally. The photocatalysis bio-adsorbent has the advantages of being high in photocatalysis capacity, high in adsorption efficiency, low in cost, convenient to separate and recover and the like. The photocatalysis bio-adsorbent can be used for treating composite waste water containing cadmium and 2,4,6-trichlorophenol, the heavy metal cadmium and the organic pollutant 2,4,6-trichlorophenol in waste water can be removed at the same time, and adsorption degradation efficiency is high.
Owner:HUNAN UNIV

Method for preparing humic acid bio-fertilizer from lignite

The invention provides a method for preparing a biological fertilizer by brown coal humic acid. With phanerochaete chrysosporium CICC40719 as a starting strain; 100-300ml solution containing 0.3% of KH2PO4, 0.15%g of MgSO4 7H2O, 0.01% of vitamin B1, 5% of pulverized brown coal and 94.54% of deionized water is inoculated with the phanerochaete chrysosporium, which is cultured by a shaking table atthe temperature of 28 DEG C for 96 hours to prepare a bacterial culture suspension I; another 100-300ml solution containing 0.3% of KH2PO4, 0.15%g of MgSO4 7H2O, 0.01% of vitamin B1, 10% of pulverized brown coal and 89.54% of deionized water is inoculated with 5% of the bacterial culture suspensionI to prepare a bacterial culture suspension II; another 100-300ml solution containing 0.3% of KH2PO4, 0.15%g of MgSO4 7H2O, 0.01% of vitamin B1, 15% of pulverized brown coal and 84.54% of deionized water is inoculated with 5% of the bacterial culture suspension II which is cultured by the shaking table to prepare a bacterial culture suspension III which is separated and purified to obtain a phanerochaete chrysosporium acclimatized strain. A culture medium is inoculated with the culture medium and cultured for 24 hours, and fermentation broth is prepared. The brown coal is pulverized by a pulverizer and sieved by a 30-mesh sieve to obtain pulverized coal, which is added with water for regulating the moisture content of the pulverized coal to 35-40%, 12-15% of ammonia water (wet basis), and 2% of rice hull (wet basis), the wet pulverized coal is stirred evenly, spread out indoors to a thickness of 8cm, and thermostatically cultured at the temperature of 28 DEG C for 30 hours, then sulfuric acid solution with 8% percentage concentration is used for neutralizing the degraded pulverized brown coal, the pH value of which is adjusted between 6.5 and 7.5, after being dried with hot air at the temperature of 55 DEG C and pulverized, the biological fertilizer is prepared.
Owner:黑龙江省宏达生物工程有限公司
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