A method of sorbing a PFAS compound from a contaminated environment can include admixing a modified clay sorbent with the environment. The modified clay can include a clay intercalated with a blend of mono-quaternary amine compound and di-quaternary amine compound.

Platforms, platform systems, and safety grates and related methods used to facilitate the installation of plant-based remediation systems are provided therein. A platform system can include a platform having a frame supporting a flooring structure that has a surface on which a worker can stand. The platform and flooring structure can have central aperture therein. The platform system can also include a sleeve frame positioned proximal to the central aperture. The sleeve frame can have sleeve clamps securable thereto for holding a sleeve ring round at least a portion of the central aperture and to hold a liner sleeve to the sleeve ring. Further, the platform system can also include a safety grate attachable to the platform. The safety grate can comprise a grid of crossbars with folding funnel guideboards secured to the grid of crossbars for funneling soil when backfilling the liner sleeve once the liner sleeve is placed in an excavated hole.

A ground water contamination remediation process includes the steps of identifying a source and location of land-based ground water contamination and excavating the soil above and within the location of the contamination to create a void. The width and depth of the void is increased to a predetermined size until the contaminated ground water is exposed creating a man-made treatment lake by allowing the contaminated ground water to partially fill the void. In one embodiment, the water in the treatment lake is aerated to reduce the amounts of hydrogen sulfide, methane, and biodegradable compounds in the contaminated water. In another embodiment, an adsorbent material is added to the treatment lake so to isolate per- and poly-fluoroalkyl substances (PFAS). The adsorbent material is applied to or mixed into PFAS contaminated water, PFAS is adsorbed, and the solid adsorbent materials settle to the bottom of the lake for subsequent management or removal.

An in-situ reagents injection system comprises a compressed air storage tank, a remediation reagents storage tank, an injection adjusting valve, an injection pipe, an upper sealing device and a lower sealing device. When the reagents injection is carried out, the compressed air is injected before the remediation reagents is injected, the porosity of the aquifer medium is increased by utilizing the air pressure expansion technology to form a relatively uniform dominant channel, and the remediation reagents is injected to realize uniform and efficient conveying of the reagents. The in-situ reagents injection system and method can make the homogeneous and efficient conveying of the remediation reagents, and ensure the full utilization of the remediation reagents, with low energy consumption of injection equipment, simple process, and flexible operation. The injection is performed in sections from top to bottom according to the steps to improve the in-situ reagents injection efficiency and remediation efficiency.

A graphene coated crushed glass particle adsorbent is provided for the removal of heavy metals and other contaminants in from solutions such as wastewaters, contaminated surface water and groundwater. The adsorbent comprises crushed (e.g. recycled) glass coated with graphene nano-sheets using a staged thermal binding process and the silicas in the glass as a catalyst. The adsorbent may be configured for use in both in-situ and ex-situ treatment systems and is capable of removing heavy metals and other inorganic and organic contaminants. The strong adsorptive bond between contaminants and the graphene coating on crushed glass particles can also lead to alternative applications of the end of life adsorbent, such as base material in road and pavement (e.g. cement-like) construction materials.

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 and enhancements for the decontamination of water containing one or more PFAS contaminants includes introducing a foaming agent into the water, and injecting a gas through a diffuser and into the water so as to form a plurality of bubbles in the water, the one or more PFAS contaminants accumulating on the plurality of bubbles. The plurality of bubbles is allowed to rise, forming a foam at the surface of the water. The resulting foam is then collected and transported away from the surface of the water, where it condenses into a liquid and is treated to regulatory standards.

Formulations and methods for destroying dense non-aqueous phase liquids (DNAPLs) using in situ chemical oxidation (ISCO) are provided. In particular, the invention provides slow release formulations comprising oxidants such as percarbonate and persulfate that efficiently destroy DNAPLs e.g. at sites requiring clean-up due to the presence of toxic DNAPL contaminants.

Methods for increasing hydrophobicity of native water-bearing zones or aquifers comprising the step of permanently embedding non-degradable, solid colloidal materials formed to have a particulate size of less than 10 microns. Exemplary materials include activated carbon, zeolites and hydrophobically treated clays. The particulate colloidal materials are coated with an agent to facilitate their distribution, including anionic polymers, chelating agents or combinations thereof. The materials are applied preferably by low pressure injection and are particularly effective at containing the migration of hydrocarbon contaminants, typically present as a plume, for at least several decades.