C02F2103/06

IRRIGATION DEVICE
20170238482 · 2017-08-24 ·

An irrigation device (10) including a solar collector (18) connected to a heating element (14). The heating element is embedded in a hydrated medium and heats this to produce water vapour. A semi-permeable membrane (34) allows the heated water vapour to be used for irrigation, thereby allowing marsh or sea water to be used to irrigate large tracts of arid soil.

A PROCESS FOR THE DETECTION AND ADSORPTION OF ARSENIC

The present invention relates to a process for the detection and adsorption of arsenic from ground water and industrial waste water using lanthanide doped nanoparticles. More particularly, the present invention provides a process for the detection and adsorption arsenic in ppm level using Eu.sub.0.05Y.sub.0.95PO.sub.4 nanoparticles.

TREATMENT OF WATER WITH UV/CHLORINE ADVANCED OXIDATION

A process for decontaminating a contaminated aqueous liquid comprising methyl-tert-butyl ether (MTBE) involving pretreating the contaminated aqueous liquid with chlorine and/or a hypochlorous acid salt and irradiating the aqueous liquid with an ultraviolet wavelength to produce a radical molecular species that degrades the MTBE. MTBE is degraded into at least one degradation byproduct including tert-butyl formate (TBF), tert-butyl alcohol (TBA), acetone, carbon dioxide, and water.

Chemical Oxidation and Biological Attenuation Process for the Treatment of Contaminated Media
20170239699 · 2017-08-24 ·

Chemically oxidizing a wide range of targeted contaminants in soils, sludges, groundwater, process water, and wastewater and assisting in the eventual (over time) biological attenuation of the contaminants utilizing persulfates activated by trivalent metals, such as ferric iron. The use of trivalent metal activated persulfate results in a chemical oxidation process that yields degradation compounds which facilitate further attenuation via biological processes.

GROUNDWATER REMEDIATION SYSTEMS, DEVICES, AND METHODS
20170232488 · 2017-08-17 ·

A liquid treatment system includes: a filter casing including a structural wall, a first screen formed though the structural wall, and a second screen formed though the structural wall; and a liquid treatment cartridge configured for placement in the filter casing between the first and second screens. The liquid treatment cartridge includes a cartridge casing having an upper end and a lower end, and an inflatable seal surrounding the cartridge casing at an intermediary position between the upper end and lower end. A method of servicing a groundwater treatment installation includes: vertically displacing a liquid treatment cartridge within a filter casing having a structural wall, a first screen formed though the structural wall, and a second screen formed though the structural wall.

Efficient and Regenerable Nano Manganese Remover, and Preparation Method and Application Thereof
20220306492 · 2022-09-29 ·

The present disclosure discloses an efficient and regenerable nano manganese remover, and a method for preparing same and application thereof, belonging to the technical field of wastewater treatment and reuse. The manganese remover of the present disclosure includes Fe.sub.3O.sub.4, RGO, SiO.sub.2 and EDTA. The Fe.sub.3O.sub.4 nanoparticles are supported on the surface of the RGO, the SiO.sub.2 coats the Fe.sub.3O.sub.4, and the EDTA is grafted on the SiO.sub.2. First, Fe.sub.3O.sub.4-RGO is prepared. Then, a TEOS-ethanol solution is dropwise added, and the resulting mixture is allowed to react to obtain Fe.sub.3O.sub.4@SiO.sub.2-RGO composite particles. Finally, an EDTA-water solution is dropwise added to obtain the manganese remover. The manganese remover prepared in the present disclosure is magnetic, and the preparation process is simple and easy for industrial production. The nano manganese remover can quickly remove manganese in manganese-containing wastewater. A small amount of the manganese remover can achieve a large adsorption capacity. Further, the nano manganese remover can be separated from the manganese-containing wastewater quickly, thereby avoiding secondary pollution to the system.

SYSTEM AND METHOD FOR BIOREMEDIATION OF SOIL
20220032350 · 2022-02-03 ·

Systems and methods for performing bioremediation using the Geobacillus sp. bacterial strain are provided which are capable of effectively degrading Benzo[a]pyrene (BaP) and efficiently degrading other ring-based organic contaminants. The exemplary bioremediation methods include steps for administering an effective, degrading amount of the bacteria to soil containing excess amounts of BaP and incubating the bacteria administered to the soil at a given temperature and for a duration that are suitable for promoting incubation and reducing and the concentration of BaP below a maximum concentration, as might be specified by a regulatory body.

BIOMEDIATION METHOD
20170225989 · 2017-08-10 ·

A method for enhancing in situ bioremediation of a volume containing groundwater and a quantity of contaminant, the method comprising the steps of: quantifying the mass of the contaminant; and amending the volume by adding thereto a compound that provides a source of NO.sub.3.sup.−. The method is characterized in that the compound is added such that the mass of the NO.sub.3.sup.− source is provided at the ratio of about 1 mg NO.sub.3.sup.− per 0.21 mg contaminant. The contaminant can be BTEX or petroleum-related VOC.

Filter media for removal of Arsenic from Potable Water with iron-impregnated activated carbon enhanced with titanium oxide
20170225968 · 2017-08-10 ·

A filter media for the filtration of potable water; specifically, for the removal of arsenic from potable water using iron-impregnated activated carbon enhanced with titanium oxide, such as the titanium oxide mixture used in the commercial product Metsorb®. The activated carbon is subjected to a wet impregnation process using an iron salt solution of approximately 6% of iron(III) chloride FeCl.sub.3 solution and 1.25% of NaOH solution.

IN-SITU REMEDIATION OF SULFATE CONTAMINATION

The present disclosure provides an in-situ method for removing sulfates. The method comprises delivering at least one low molecular weight organic compound (LMWOC) to soil or groundwater to attain a concentration of the LMWOC of 750-3000 mg/L, such as 1000-2000 mg/L, or about 1500 mg/L, especially whereby sulfate is reduced to below 250 mg/L in the soil or groundwater. The method may further comprise contacting the soil or groundwater with an oxidizer, such as hydrogen peroxide, whereby the concentration of metals or metalloids is reduced in the soil or groundwater.