An ecosystem for deep water environment restoration includes: a light-collecting device; an underwater lighting system connected to the light-collecting device and configured to provide light to a deep water layer of a water body; a photocatalytic bionic net comprising a photocatalytic material and a fiber and placed in the deep water layer; and an aquatic plant. When the photocatalytic material receives the light, the photocatalytic material is able to adsorb organic pollutants of the water body to the photocatalytic bionic net and catalyze degradation of the organic pollutants of the water body, concentrate microorganisms to allow the microorganisms to decompose the organic pollutants into nutrients required for growth of the aquatic plant, and absorb the light to catalyze decomposition of water to produce oxygen. When the aquatic plant receives the light, the aquatic plant is able to perform photosynthesis to release oxygen.

An ecosystem for deep water environment restoration includes: a light-collecting device; an underwater lighting system connected to the light-collecting device and configured to provide light to a deep water layer of a water body; a photocatalytic bionic net comprising a photocatalytic material and a fiber and placed in the deep water layer; and an aquatic plant. When the photocatalytic material receives the light, the photocatalytic material is able to adsorb organic pollutants of the water body to the photocatalytic bionic net and catalyze degradation of the organic pollutants of the water body, concentrate microorganisms to allow the microorganisms to decompose the organic pollutants into nutrients required for growth of the aquatic plant, and absorb the light to catalyze decomposition of water to produce oxygen. When the aquatic plant receives the light, the aquatic plant is able to perform photosynthesis to release oxygen.

The present invention provides methods of stopping a larva of a sessile invertebrate in a settlement stage from swimming or crawling in water, by means of irradiating violet light having a wavelength range of 400 to 550 nm to the larva in the settlement stage of the sessile invertebrate.

The present invention provides methods of stopping a larva of a sessile invertebrate in a settlement stage from swimming or crawling in water, by means of irradiating violet light having a wavelength range of 400 to 550 nm to the larva in the settlement stage of the sessile invertebrate.

An annular bubbling electric discharge reactor for treating water includes a non-conductive pipe having a top and a bottom with a gas sparger installed within the non-conductive pipe and positioned adjacent the bottom and adapted to generate bubbles or foam and control the bubble size formation. A high voltage electrode is fixed concentrically within the non-conductive pipe and a ground electrode is fixed at an intermediate position within the non-conductive pipe and in circumferential relation to the high voltage electrode with an annular space defined between the ground electrode and high voltage electrode. A liquid inlet and a liquid outlet are provided to allow polluted liquid/water into the reactor and discharge treated liquid/water therefrom. A circuit and power supply are provided for generating an electrical discharge between the high voltage electrode and ground electrode, thereby creating a plasma generation region where the liquid is treated.

An annular bubbling electric discharge reactor for treating water includes a non-conductive pipe having a top and a bottom with a gas sparger installed within the non-conductive pipe and positioned adjacent the bottom and adapted to generate bubbles or foam and control the bubble size formation. A high voltage electrode is fixed concentrically within the non-conductive pipe and a ground electrode is fixed at an intermediate position within the non-conductive pipe and in circumferential relation to the high voltage electrode with an annular space defined between the ground electrode and high voltage electrode. A liquid inlet and a liquid outlet are provided to allow polluted liquid/water into the reactor and discharge treated liquid/water therefrom. A circuit and power supply are provided for generating an electrical discharge between the high voltage electrode and ground electrode, thereby creating a plasma generation region where the liquid is treated.

A system using electrical discharge plasma (EDP) for treating a liquid, such as water or waste water to degrade or destroy polar contaminants such as per- and polyfluoroalkyl substances (PFAS) compounds, the system includes a sealed process tank and multiple submerged EDP channels stacked horizontally. Each EDP channel consists of a cathode and an anode, a gas hood, and a gas diffuser. The basic submerged EDP channel is bounded by a plate at the bottom and a submerged gas hood at the top which creates a gas headspace, and hence, a local water surface to provide a local gas/liquid interface in each channel. The cathode lies above the local water surface and anode lies below the local water surface. Each EDP channel may have a gas diffuser at the bottom of the EDP channel for introducing a process gas into the liquid creating bubbles that carry contaminants in the liquid to the local gas/liquid interface. An electrical discharge arcs between the cathode and the anode to generate a plasma used for destruction of contaminants in the water or wastewater at the local gas/liquid interface.

A system using electrical discharge plasma (EDP) for treating a liquid, such as water or waste water to degrade or destroy polar contaminants such as per- and polyfluoroalkyl substances (PFAS) compounds, the system includes a sealed process tank and multiple submerged EDP channels stacked horizontally. Each EDP channel consists of a cathode and an anode, a gas hood, and a gas diffuser. The basic submerged EDP channel is bounded by a plate at the bottom and a submerged gas hood at the top which creates a gas headspace, and hence, a local water surface to provide a local gas/liquid interface in each channel. The cathode lies above the local water surface and anode lies below the local water surface. Each EDP channel may have a gas diffuser at the bottom of the EDP channel for introducing a process gas into the liquid creating bubbles that carry contaminants in the liquid to the local gas/liquid interface. An electrical discharge arcs between the cathode and the anode to generate a plasma used for destruction of contaminants in the water or wastewater at the local gas/liquid interface.

Water purification particles have porous particles and photocatalyst particles formed of titanium-based compound particles that are supported on the porous particles, have absorption at a wavelength of 500 nm in a visible absorption spectrum, and have an absorption peak at 2,700 cm.sup.−1 to 3,000 cm.sup.−1 in an infrared absorption spectrum, and a metal compound having a metal atom and a hydrocarbon group is bonded to the surface of each of the titanium-based compound particles through an oxygen atom.

Water purification particles have porous particles and photocatalyst particles formed of titanium-based compound particles that are supported on the porous particles, have absorption at a wavelength of 500 nm in a visible absorption spectrum, and have an absorption peak at 2,700 cm.sup.−1 to 3,000 cm.sup.−1 in an infrared absorption spectrum, and a metal compound having a metal atom and a hydrocarbon group is bonded to the surface of each of the titanium-based compound particles through an oxygen atom.