A method of preparing a FeMnCeO.sub.x biomaterial is provided, including the following steps. A Pseudomonas sp. strain KW-2 is obtained. A culture medium with a pH of 6.5-7.8 is prepared, which includes 0.1 g/L K.sub.2HPO.sub.4, 0.2 g/L MnSO.sub.4.Math.7H.sub.2O, 0.2 g/L NaNO.sub.3, 0.1 g/L CaCl.sub.2), 0.1 g/L NH.sub.4Cl, 0.1 g/L (NH.sub.4).sub.2CO.sub.3, 35 g/L NaCl and 150 mg/L ferric ammonium citrate. The culture medium is autoclaved, inoculated with the KW-2 strain, cultured for 1-3 days, added with a cerium nitrate solution, cultured for 3-7 days and centrifuged at 4,000-8,000 rpm for 10-20 min to collect a precipitate. The precipitate is rinsed 5-8 times with deionized water and 0.01 mol/L phosphate buffered saline (PBS) and freeze-dried at ?60? C. to obtain the FeMnCeO.sub.x biomaterial. A method for treating antibiotic wastewater using the FeMnCeO.sub.x biomaterial is also provided.

A method of preparing a FeMnCeO.sub.x biomaterial is provided, including the following steps. A Pseudomonas sp. strain KW-2 is obtained. A culture medium with a pH of 6.5-7.8 is prepared, which includes 0.1 g/L K.sub.2HPO.sub.4, 0.2 g/L MnSO.sub.4.Math.7H.sub.2O, 0.2 g/L NaNO.sub.3, 0.1 g/L CaCl.sub.2), 0.1 g/L NH.sub.4Cl, 0.1 g/L (NH.sub.4).sub.2CO.sub.3, 35 g/L NaCl and 150 mg/L ferric ammonium citrate. The culture medium is autoclaved, inoculated with the KW-2 strain, cultured for 1-3 days, added with a cerium nitrate solution, cultured for 3-7 days and centrifuged at 4,000-8,000 rpm for 10-20 min to collect a precipitate. The precipitate is rinsed 5-8 times with deionized water and 0.01 mol/L phosphate buffered saline (PBS) and freeze-dried at ?60? C. to obtain the FeMnCeO.sub.x biomaterial. A method for treating antibiotic wastewater using the FeMnCeO.sub.x biomaterial is also provided.

A three-dimensional lignin porous carbon/zinc oxide composite material and its preparation and application in the field of photocatalysis are disclosed. The method includes preparing a lignin/zinc oxide precursor composite by a hydrothermal method from a zinc salt, a weak alkali salt and an industrial lignin, and preparing a three-dimensional lignin porous carbon/zinc oxide composite material by high temperature calcination of the lignin/zinc oxide precursor composite. The composite material has a regular three-dimensional pore structure, with zinc oxide nanoparticles uniformly embedded among the three-dimensional lignin porous carbon nanosheets. Application of the composite material to the field of photocatalysis, especially as a photocatalyst for photocatalytic degradation of organic dye pollutants, can significantly improve the degradation efficiency and rate, and has potential application value in the field of photocatalytic degradation of organic pollutants.

A three-dimensional lignin porous carbon/zinc oxide composite material and its preparation and application in the field of photocatalysis are disclosed. The method includes preparing a lignin/zinc oxide precursor composite by a hydrothermal method from a zinc salt, a weak alkali salt and an industrial lignin, and preparing a three-dimensional lignin porous carbon/zinc oxide composite material by high temperature calcination of the lignin/zinc oxide precursor composite. The composite material has a regular three-dimensional pore structure, with zinc oxide nanoparticles uniformly embedded among the three-dimensional lignin porous carbon nanosheets. Application of the composite material to the field of photocatalysis, especially as a photocatalyst for photocatalytic degradation of organic dye pollutants, can significantly improve the degradation efficiency and rate, and has potential application value in the field of photocatalytic degradation of organic pollutants.

The application provides an oxide layer material capable of adsorbing and degrading methane gas, which is obtained by a method comprising the steps of: 1) subjecting a cracked household refuse to aerobic biological pretreatment; 2) subjecting the material which has been subjected to the aerobic biological pretreatment to biological stabilizing treatment; and 3) adding copper chloride, potassium sulfate, magnesium oxide, and a composite bacterial agent for oxidizing methane gas to the material which has been subjected to the biological stabilizing treatment to obtain the oxide layer material capable of adsorbing and degrading methane gas. This disclosure further discloses a method for preparing the oxide layer material capable of adsorbing and degrading methane gas described above.

Method for converting organic material into catalyst for biological hydrosynthesis, comprising providing organic material comprising at least one source of readily available carbon, at least one complex carbon-containing compound and at least one source of protein and contacting the organic material with preparatory catalyst is provided. The organic material is subjected to a size reduction process to produce size-reduced organic material and a solid to liquid ratio of the size-reduced organic material is adjusted to form organic material slurry. The organic material slurry is subjected to a fermentation process to produce amended organic material, by applying a process catalyst to at least a portion of the organic material slurry. A liquid is recovered from the amended organic material and transferred to a fermentation chamber, where it is subjected to a fermentation process to produce amended liquid by applying balancing catalyst to the liquid. The amended liquid is the catalyst.

Method for converting organic material into catalyst for biological hydrosynthesis, comprising providing organic material comprising at least one source of readily available carbon, at least one complex carbon-containing compound and at least one source of protein and contacting the organic material with preparatory catalyst is provided. The organic material is subjected to a size reduction process to produce size-reduced organic material and a solid to liquid ratio of the size-reduced organic material is adjusted to form organic material slurry. The organic material slurry is subjected to a fermentation process to produce amended organic material, by applying a process catalyst to at least a portion of the organic material slurry. A liquid is recovered from the amended organic material and transferred to a fermentation chamber, where it is subjected to a fermentation process to produce amended liquid by applying balancing catalyst to the liquid. The amended liquid is the catalyst.

A composition derived from the acid treatment of ashes obtained after heat treatment of selected plants or plant material is provided. The selected plants accumulate metal from the platinum group (platinoids). The compositions can be used to produce catalysts for performing various organic synthesis reactions.

A composition derived from the acid treatment of ashes obtained after heat treatment of selected plants or plant material is provided. The selected plants accumulate metal from the platinum group (platinoids). The compositions can be used to produce catalysts for performing various organic synthesis reactions.

The present invention relates to the field of biological sample testing technology, and in particular, to a biological sample reaction vessel. A reagent storage portion and a push rod movable relative to the reagent storage portion are packaged in the reaction vessel; the reagent storage portion comprises at least one reagent containing cavity, and the reagent containing cavity is sealed by a sealing element; and the push rod is connected to the sealing element, and the push rod is used for cooperation with an external device to separate the sealing element from the reagent storage portion. In this application, the reagent storage portion and the push rod are both packaged in the biological sample reaction vessel, and in reaction, the biological sample reaction vessel only needs to cooperate with a test cassette. With one operation, that is, inserting the biological sample reaction vessel into the external device, the reagent in the reagent storage portion can be released rapidly.