The present application is related to a method for controlling heavy metal scouring pollution in mines by using a humified product, which comprises steps of: (1) carrying out mixed fermentation on sludge and hyperthermophiles to breed polar humified groups, and then carrying out mixed fermentation on the fermented material and a native material of humus precursors to induce massive production of humus until the humus content reaches a required standard; and (2) mixing and maintaining the humified product of the sludge reaching the standard with mine soil polluted by heavy metals to remedy the polluted mine.

The present disclosure provides a method of preparing a carbonaceous material capable of fixing arsenic and an application thereof. Through biomass pretreatment, biomass pyrolysis and arsenite fixation, a biochar activated by potassium carbonate and an arsenic-containing wastewater containing sulfur-containing substances are mixed and deoxidized, and an anaerobic culture is carried out, to fix arsenic by the biochar activated by potassium carbonate. The present disclosure solves the problems that arsenic is released from the soil and groundwater under anaerobic conditions, the ability of conventional passivatingagents to fix arsenic under anaerobic conditions is weakened, and the conventional carbonaceous materials not only cannot fix arsenic, but also accelerate the release of anaerobic arsenic.

The present disclosure provides a method of preparing a carbonaceous material capable of fixing arsenic and an application thereof. Through biomass pretreatment, biomass pyrolysis and arsenite fixation, a biochar activated by potassium carbonate and an arsenic-containing wastewater containing sulfur-containing substances are mixed and deoxidized, and an anaerobic culture is carried out, to fix arsenic by the biochar activated by potassium carbonate. The present disclosure solves the problems that arsenic is released from the soil and groundwater under anaerobic conditions, the ability of conventional passivatingagents to fix arsenic under anaerobic conditions is weakened, and the conventional carbonaceous materials not only cannot fix arsenic, but also accelerate the release of anaerobic arsenic.

The invention relates to a method for disinfecting soils or other agricultural growing media, characterised by comprising the following steps: obtaining a soil or other agricultural growing medium at their field capacity; treating the soil or medium at the field capacity of the previous step with ozonated water, wherein the ozonated water is prepared in situ with ozone-production equipment connected to the water supply; allowing a period of time to pass after the treatment with ozone; and inoculating the disinfected soil or agricultural medium with at least one species of beneficial microorganism.

The invention relates to a method for disinfecting soils or other agricultural growing media, characterised by comprising the following steps: obtaining a soil or other agricultural growing medium at their field capacity; treating the soil or medium at the field capacity of the previous step with ozonated water, wherein the ozonated water is prepared in situ with ozone-production equipment connected to the water supply; allowing a period of time to pass after the treatment with ozone; and inoculating the disinfected soil or agricultural medium with at least one species of beneficial microorganism.

A method for degrading a polycyclic aromatic hydrocarbon such as the 5-membered ring compound benzo(a)pyrene (BZP) using a halophilic microbe Staphylococcus haemoliticus, strain 10SBZ1A.

A composition for remediation of soil and groundwater containing halogenated compounds. The remediation composition includes an elemental iron-based composition, which may include activated carbon capable of absorbing the halogenated compounds with numerous pores impregnated with elemental iron. The remediation composition further includes a first bioremediation material including a blend of one-to-many organisms capable of degrading the halogenated compounds. The remediation composition includes an organic compound or polymeric substance and a second bioremediation material including a blend of one-to-many organisms capable of degrading the organic compound or polymeric substance over time (e.g., 20 to 365 or more days to provide a time release substrate-creating material or platform) into smaller molecules or compounds used by the organisms in the first bioremediation material while degrading the halogenated compounds. The organic compound may be a complex carbohydrate such as food grade starch, chitin, or other complex carbohydrate such as one with low water solubility.

A composition for remediation of soil and groundwater containing halogenated compounds. The remediation composition includes an elemental iron-based composition, which may include activated carbon capable of absorbing the halogenated compounds with numerous pores impregnated with elemental iron. The remediation composition further includes a first bioremediation material including a blend of one-to-many organisms capable of degrading the halogenated compounds. The remediation composition includes an organic compound or polymeric substance and a second bioremediation material including a blend of one-to-many organisms capable of degrading the organic compound or polymeric substance over time (e.g., 20 to 365 or more days to provide a time release substrate-creating material or platform) into smaller molecules or compounds used by the organisms in the first bioremediation material while degrading the halogenated compounds. The organic compound may be a complex carbohydrate such as food grade starch, chitin, or other complex carbohydrate such as one with low water solubility.

A composition for stimulating the production and excretion of a lignolytic enzyme in a microorganism for degrading harmful substances and/or in the manufacturing of easily degradable ester containing plastics or articles made of ester containing plastic. The composition mainly includes tributyrin, triolein, fish oil, 16-hydroxyhexadecanoic acid, n-aliphatic primary fatty alcohols, polycaprolactone, aliphatic polyesters, linolenic acid, linoleic acid, alpha linolenic acid, plant polyesters, cutin, cutin derivatives, cutin monomers, omega hydroxy acids, 16-hydroxy palmitic acid, 9,16-dihydroxypalmitic acid, 10,16-dihydroxypalmitic acid, C18-hydroxy oleic acid, 9,10-epoxy-18-hydroxy stearic acid, 9,10,18-trihydroxystearate, suberin, cork, fruit skins, vegetable skins, and their constituents and derivatives, hydroxy fatty acids, 16-hydroxy palmitic acid, 18-hydroxy stearic acid, juniperic acid, hexadecanol, linseed oil, perilla oil, amides, acetamide and N-acetyl amide, zinc, zinc salts, butyrate, acetate, lactate, manganese peroxidase, and carbamide peroxide.

A method for biological hydrosynthesis, energy generation and storage and/or topsoil restoration comprising the steps of: undertaking a primary amendment of a site with a first catalyst and a second catalyst, wherein the first catalyst and the second catalyst are applied to at least a portion of the site such that a matrix of biological energy generation points are constructed on about 5% of the site by area; undertaking a secondary amendment of the site with the first catalyst and the second catalyst, wherein the first catalyst and the second catalyst are applied to at least a portion of the site such that a matrix of biological energy generation points are constructed on about 20% of the site by area, and undertaking a tertiary amendment of the site with the first catalyst and the second catalyst, wherein the first catalyst and the second catalyst are applied to at least a portion of the site such that a matrix of biological energy generation points are constructed on about 75% of the site by area, wherein the primary amendment, the secondary amendment and the tertiary amendment of the site are each conducted at least once.