The present disclosure relates to methods of synthesizing slurries comprising ferrihydrite nanoparticles, and systems and methods employing the same. The method may include the steps of preparing an aqueous solution having ferric iron cations, halide anions, and a two-line iron promoter, and precipitating the ferrihydrite nanoparticles in the aqueous solution, thereby producing a ferrihydrite slurry. The ferrihydrite slurries may be useful in treating a polluted fluid having sulfur contaminants therein.

Provided herein is a cesium adsorbent including: a support modified to have a carboxyl group on a surface thereof; and Prussian blue synthesized on the surface of the modified support, wherein the Prussian blue is at least partially chemically bound with the surface of the support. The cesium adsorbent may effectively adsorb cesium, which is a radioactive element released into the water and may be easily prepared using a simple solution process.

An active element for trapping and/or releasing a gaseous or liquid substance is provided including a solid body, which is enveloped by an outer boundary surface (S), and contains an active material adapted to trap and/or release a gaseous or liquid substance, wherein the outer boundary surface S has an overall roundish, preferably round shape. The active element is manufactured by injection moulding and can be utilized within a container.

A magnetic adsorbent, preparation method therefor and application thereof. The magnetic adsorbent is made by loading a weakly material with high adsorption capacity, an iron-based gel, onto a strongly magnetic ferrite material with low adsorption capacity by means of in-situ reaction. The magnetic adsorbent is used for removing heavy metal pollutants and phosphate pollutants from water.

The invention provides biocomposites alginate/chitosan beads integrated with magnetite nanoparticles and modified-surface magnetite derivate created and designed to remove from environmental waters and aquatic systems different types of organic persistent compounds such as benzophenone-3 (oxybenzone).

Multi-functional materials for use in reversible, high-capacity hydrogen separation and/or storage are described. Also described are systems incorporating the materials. The multi-functional materials combine a hydrogen-absorbing material with a high-efficiency and a non-contact energy-absorbing material in a composite nanoparticle. The non-contact energy-absorbing material include magnetic and/or plasmonic materials. The magnetic or plasmonic materials of the composite nanoparticles can provide localized heating to promote release of hydrogen from the hydrogen storage component of the composite nanoparticles.

Systems, devices, and techniques described herein relate to iron-based desalination of water. In some cases, an inflow of water including chlorine and sodium can be received. A plurality of iron nanoparticles may capture the chlorine and the sodium. The iron nanoparticles may at least partially include Zero Valent Iron (ZVI). An outflow of the water may be emitted. The chlorine and the sodium may be omitted from the outflow.

The present disclosure provides for a method for producing porous granular composite iron having high permeability, hydrophilicity, reactivity, and capacity for treatment of inorganic and organic contaminants. The method may include the steps of: mixing iron powder, or iron/metal mixture and adsorbent powders, with surface modifier and binder compounds to form a granular material. This granular material is used in a filter, vessel, and in situ permeable reactive barrier by passing a contaminated liquid stream through a bed of the granular product for removal of the contaminants. The porous granular iron materials have low bulk density, do not fuse together and can be regenerated for reuse.

The invention relates to a material for storing and releasing oxygen, consisting of a reactive ceramic made of copper, manganese and iron oxides, wherein, subject to the oxygen partial pressure of a surrounding atmosphere and/or an ambient temperature, the reactive ceramic has a transition region that can be passed through any number of times, said transition region being between a discharge threshold state of a three-phase crednerite/cuprite/hausmannite mixed ceramic and a charge threshold state of a two-phase spinel/tenorite mixed ceramic. A passing through of the transition region from the discharge threshold state towards the charging threshold state is associated with oxygen uptake and a passing through of the transition region from the charge threshold state towards the discharge threshold state is associated with oxygen release.

Water insoluble carbonates are utilized as adsorbents to remove phosphates from water flowing through an iron impregnated or coated foam. The iron impregnated or coated foam acts to improve the removal of phosphates as well as to remove nitrates and ammonia. A powdered carbonates/binder mixture, i.e. MgCO.sub.3 and/or La.sub.2(CO.sub.3).sub.3 mixed with cellulose, is formed into pellets then calcined. Aqueous phosphates adsorb onto the surface area of the pellet for eventual removal. Calcining the pellets removes the cellulose binder and opens the interior of the pellet up to provide additional surface area for adsorption. These pellets are placed within a porous bag and placed with water, preferably within a flow of water.