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201 results about "Iron(II) sulfide" patented technology

Iron(II) sulfide or ferrous sulfide (Br.E. sulphide) is one of a family chemical compounds and minerals with the approximate formula FeS. Iron sulfides are often iron-deficient non-stoichiometric. All are black, water-insoluble solids.

Preparation method and applications of ferrous sulfide/biological carbon composite material

The present invention discloses an efficient ferrous sulfide / biological carbon composite material and a preparation method thereof, and applications of the ferrous sulfide / biological carbon composite material in repair of heavy metal pollution water bodies. According to the present invention, biological carbon is adopted as a carrier, a ferrous sulfate solution and the biological carbon are mixed, sodium carboxymethyl cellulose is added as a stabilizer and a dispersant, a sodium sulfide solution is added to the system in a dropwise manner under the nitrogen protection, and vigorous stirring is performed to make the generated ferrous sulfide nanoparticles uniformly grow on the surface of the biological carbon, such that the disadvantage that the ferrous sulfide nanoparticles are easily agglomerated is substantially improved so as to increase the effective contact area between the ferrous sulfide nanoparticles and the pollutant, and the adsorption ability and the oxidation reduction ability of the ferrous sulfide and the biological carbon are integrally combined so as to improve the pollutant removal ability; the preparation method has advantages of simple and rapid process, low production cost, environmental protection and no secondary pollution; and the efficient ferrous sulfide / biological carbon composite material can strongly repair the Cr(VI) polluted water body, can effectively reduce the biological toxicity of the Cr(VI) on wheat seeds, and has wide application prospects in the fields of repair of organic pollution and inorganic pollution in environments.
Owner:NANKAI UNIV

Method for synchronously removing nitrogen and phosphorus in sewage containing nitrogen and phosphorus

The invention discloses a method for synchronously removing nitrogen and phosphorus in sewage containing nitrogen and phosphorus, belonging to the field of sewage treatment. The method comprises the steps of (1) screening thiobacillus denitrificans: screening thiobacillus denitrificans from anaerobic activated sludge and taking as target strain, wherein thiobacillus denitrificans utilizes sulphur source in ferrous sulfide to conduct autotrophic denitrification; (2) preparing fillers of a reactor: directly adding ferrous sulfide with the particle size smaller than 25mm in a reaction container; (3) adding sewage: feeding sewage to be treated into the reaction container, wherein the sewage to be treated is the sewage containing nitrogen and phosphorus with the pH value of 5.0-9.0; (4) conducting the autotrophic denitrification process: conducting the mixed reaction for 2 to 6d at the temperature of 10 DEG C-40 DEG C under the anaerobic condition in the reaction container, reducing NO2<-> and NO3<-> in water to be N2 by thiobacillus denitrificans while simultaneously oxidizing ferrous sulfide by thiobacillus denitrificans, and simultaneously, precipitating phosphorus in water by utilizing iron ions (being oxidation products); and (5) separating solid and liquid. According to the method, the technology for removing nitrogen by utilizing thiobacillus denitrificans and the technology for removing phosphorus by using iron ions are fused naturally, the reaction cost is low, and the processing effect is good.
Owner:NANJING UNIV

Ferrous sulfide dirt neutral complexing cleaning agent and preparation method thereof

The invention relates to an equipment cleaning agent which is used in the field of petroleum and chemical industry, in particular to a ferrous sulfide dirt neutral complexing cleaning agent which is used for washing a synthesized ammonia low-temperature methanol washing unit system in the petroleum chemical industry and the coal chemical industry. The ferrous sulfide dirt neutral complexing cleaning agent is prepared from the following raw materials in parts by weight: 5 to 8 parts of sodium gluconate, 7 to 11 parts of sodium salicylate, 20 to 26 parts of gadoliniam diethylene triamine pentaacetic acid, 20 to 26 parts of sodium ethylene diamine tetracetate, 40 to 46 parts of propenoic acid-itaconic acid copolymer, 25 to 32 parts of disodium polyepoxysuccinicate, 12 to 15 parts of sodium hydroxyphenylace, 3 to 7 parts of triethanolamine, 3 to 7 parts of hydrogen peroxide, 0.1 to 0.3 part of lauryl sodium sulfate, 0.1 to 0.3 part of polydimethyl siloxane fluid and 40 to 45 parts of water. The ferrous sulfide dirt neutral complexing cleaning agent is free from generating hydrogen sulfide when cleaning the ferrous sulfide dirt and corroding the equipment and has strong capacity for complexing the iron ions, the removal speed is fast, the decontamination rate is more than 98 percent, the neutralization and passivation are unnecessary to carry out after the chemical washing, and the equipment can be put into operation immediately.
Owner:GANSU HEIMA PETROCHEM ENG

Magnesium based ferrous sulfide composite nanomaterial as well as preparation method and application thereof

The invention belongs to the field of composite materials and discloses a magnesium based ferrous sulfide composite nanomaterial as well as a preparation method and application thereof. The preparation method comprises the steps: evenly dispersing magnesium based material powder into water to obtain a magnesium based material suspension, wherein a magnesium based material is at least one of magnesium oxide and magnesium hydroxide; then adding a ferrite water solution into the magnesium based material suspension, evenly mixing, dropwise adding a sodium sulfide water solution, reacting to obtainferrous sulfide and standing to obtain the magnesium based ferrous sulfide composite nanomaterial after reaction finishes. According to the preparation method disclosed by the invention, a nano ferrous sulfide material is loaded to the surface of the magnesium based material, and agglomeration of ferrous sulfide particles is inhibited to ensure reaction activity of the ferrous sulfide particles;the active surface of the magnesium based material can efficiently adsorb heavy metal, so that a utilization rate of the ferrous sulfide nanomaterial is improved; meanwhile, a weak-basicity material prepared from the magnesium based material is favorable for stable existence of the nano ferrous sulfide material, so that the composition material is not prone to metamorphosing and is easy to store.
Owner:SOUTH CHINA UNIV OF TECH

Preparation method and application of nano-silica introduced magnetic vulcanized nanometer zero-valent iron

The invention relates to a preparation method of nano-silica introduced magnetic vulcanized nanometer zero-valent iron. The preparation method comprises the concrete steps: (1) adding sodium borohydride and sodium persulfate into water to form a mixed solution; (2) adding nano-silica into a solution containing sodium borohydride and sodium persulfate and continuously stirring; (3) slowly dropwise adding a suspension formed in the second step under the stirring condition into a ferric salt solution by virtue of a peristaltic pump; and (4) after reaction is finished, carrying out solid-liquid separation by utilizing a magnet, respectively cleaning twice by adopting deionized water and anhydrous alcohol, and finally directly storing into a deionized water-alcohol solution, or vacuum drying and then storing in an anaerobic glove box. The invention also discloses environment repairing application of the nano-silica introduced magnetic vulcanized nanometer zero-valent iron. The preparation method is convenient and rapid and is low in cost and technical requirements; the material synthesized by the preparation method has the characteristics of both nanometer zero-valent iron and nanometer ferrous sulfide, is capable of solving the problems that the synthesized material is nonmagnetic, easily oxidized and difficultly applied in the absence of nano-silica, is excellent in inorganic and organic pollutant removing performances and has wide application prospect.
Owner:TONGJI UNIV

Sulfur-series medium-high entropy MAX phase solid solution material as well as preparation method and application of same

InactiveCN112094121AHigh purityFavorable control of synthetic pathwaysNuclear powerPhysical chemistry
The invention discloses a sulfur-series medium-high entropy MAX phase solid solution material as well as a preparation method and application of the same, wherein the M position of the sulfur-series medium-high entropy MAX phase solid solution material comprises any three or a combination of more than four of transition metal elements Ti, Zr, Hf, V, Nb and Ta, the A position is a sulfur element, and the X position is a carbon element. The preparation method comprises the steps that ferrous sulfide serves as a high-temperature solid sulfur source, transition metal sulfide is obtained through areplacement reaction between transition metal simple substances and the ferrous sulfide, then the transition metal sulfide reacts with metal carbide, and the sulfur-series medium-high entropy MAX phase solid solution material is obtained. The ferrous sulfide sulfur source and the sulfur-containing intermediate product adopted by the invention are both stable metal sulfides, so that volatilizationof elemental sulfur in the high-temperature preparation process is avoided, and the synthesis path of a target phase is favorably controlled. The sulfur-series medium-high entropy MAX phase solid solution material is expected to have a good application prospect in the field of extreme environment structural materials such as nuclear power and high-speed rails.
Owner:宁波材料所杭州湾研究院 +1

Chemical stabilization repair method of lead contaminated soil

The invention relates to a chemical stabilization repair method of lead contaminated soil. The chemical stabilization repair method comprises the steps that (1) ferrous sulfide particle suspension liquid is prepared; (2) the lead contaminated soil is pretreated, wherein the lead contaminated soil is crushed and sieved to obtain soil with the particle size smaller than 10 cm; (3) chemical stabilization treatment of the first time is carried out, a sodium phosphate solution and a sodium chloride solution are added into the soil treated through the step (2), the water content of the soil is keptbetween 30% to 50%, and after uniform stirring and mixing, moisture preserving maintenance is carried out for 2 days to 5 days; and (4) chemical stabilization treatment of the second time is carried out, calcium carbonate and the ferrous sulfide particle suspension liquid prepared in the step (1) are added into the soil treated in the step (3), the water content of the soil is kept between 40% to60%, after uniform stirring and mixing, moisture preserving maintenance is carried out for 1 week to 3 weeks, and the repaired soil is obtained. The combined repair method is provided and is combinedwith the advantages of multiple repair agents, the treatment effect of the lead contaminated soil is improved, secondary contamination is relieved, and the TCLP leaching quantity of lead in the treated soil can be reduced to be 0.25 mg/L or below.
Owner:重庆市环境科学研究院 +1

Preparation method and application of chitosan-stabilized zirconium-modified nanometer ferrous sulfide composite material

The invention provides a preparation method and application of a chitosan-stabilized zirconium-modified nanometer ferrous sulfide composite material, belonging to the technical field of environmentally functional composite nanomaterials. The preparation method specifically comprises the following steps: firstly, preparing zirconium oxide with controllable granularity and relatively high purity by adopting a sol method, and dissolving chitosan by using a dilute acid solution; and adding a ferrous chloride solution into the obtained chitosan solution under the protection of nitrogen, carrying out uniform stirring, adding the zirconium oxide sol, continuing stirring, dropwise adding a sodium sulfide solution, conducting reacting, and performing standing to obtain the chitosan-stabilized zirconium-modified nanometer ferrous sulfide composite material. The material is synthesized by adopting a one-step coprecipitation method, raw material cost is low, a preparation process is simple, the defects that ferrous sulfide is easy to agglomerate, low in reaction activity and poor in stability are overcome, meanwhile, the material has a more stable removal effect on molybdate in water, and the material has a good market application prospect in treatment of molybdenum pollution of surface water and underground water.
Owner:ANHUI UNIVERSITY OF TECHNOLOGY

Treatment method of water polluted by mercury

The invention relates to the field of water treatment, and in particular relates to a treatment method of water polluted by mercury. The method comprises the following steps: (1) regulating the pH value of mercury-containing sewage to be 6-6.5, and adding sodium alcohol ether sulfate and sodium hypochlorite into the mercury-containing sewage, wherein the additive amount of sodium alcohol ether sulfate accounts for 1-2 times of the mass concentration of mercury in the sewage, and the additive amount of sodium hypochlorite accounts for 3-5 times of the mass concentration of mercury in the sewage; (2) regulating the pH value of the sewage to be 8-9, and then adding poly p-tert-butylphenol disulfide, ferrous sulfide and sodium hydrogen sulfate into the sewage under the conditions that the mass ratio of p-tert-butylphenol disulfide to ferrous sulfide to sodium hydrogen sulfate is (1-2) to (2-4) to 5, and the mass concentration of poly p-tert-butylphenol disulfide in the sewage is 1-5%; (3) then adding a flocculating agent, calcium oxide and alkylphenol polyoxyethylene into the sewage under the conditions that the mass ratio of the flocculating agent to calcium oxide to alkylphenol polyoxyethylene is 1 to 3 to 2, and the additive quantity of the flocculating agent is 0.1-0.3% of the quantity of the sewage; (4) standing the sewage for 3-5 days in a separation tank, and then performing solid-liquid separation; (5) adsorbing the separated sewage by adopting an activated carbon absorber, and then discharging the sewage.
Owner:ZHEJIANG OCEAN UNIV
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