The present invention relates to floating lakes and to the treatment of the water in such lakes. The present invention further relates to large floating lakes that can be installed within a natural or artificial water body to improve water conditions that are unsuitable for recreational uses. The floating lake can be provided with a chemical application system; a filtration system including a mobile suctioning device and filters; a skimmer system, and optionally a coordination system.

A water treatment equipment includes a reaction chamber, a waveform generator, and a controller. The reaction chamber includes a pipe having a first electrode and a second electrode. The first and second electrodes are coupled to a waveform generator. The reaction chamber includes a water inlet, and a water outlet. The waveform generator is coupled to the first and second electrodes. The waveform generator is configured to generate an electrical current with a frequency that is substantially equal to the electrical resonance of the pipe of the reaction chamber. The controller is configured to control the waveform generator, wherein the reaction chamber is configured to enable a flow of ozone and water to be treated through the pipe.

An embodiment method includes generating a first water product and a sludge of contaminants from water to be treated using an advanced electronic-oxidation process. The advanced electronic-oxidation process includes an electronic treatment comprising a combination of electrocoagulation, electro-flocculation, electro-chlorinator, and electro-dialysis operated in synchronization with ozone. The method further includes separating the sludge of contaminants from the first water product using a filtration process, and filtering the first water product to produce a second water product and a concentrated water byproduct. The filtering includes a first sub-stage to remove particles greater than 0.02 m to about 0.05 m followed by a second sub-stage that includes a reverse osmosis process or a nano-filtration process. The second water is exposed product to an ultraviolet light treatment or ozonation process to generate clean water.

A method of reducing the organic compounds in an aqueous stream by generating an oxidant in-situ using at least one electrolytic cell. The method may comprise contacting at least a portion of the aqueous stream with the electrolytic cell. The electrolytic cell may have at least two electrodes, wherein at least one electrode is a metal electrode and, a power source for powering the at least two electrodes. A water treatment system for generating an oxidant in-situ comprising at least one electrolytic cell. The electrolytic cell may have at least two electrodes, wherein at least one electrode is a metal electrode, and a power source for powering the at least two electrodes. A method of improving the rejection rate of a reverse osmosis membrane using an oxidant generated in-situ. The method may comprise contacting at least a portion of the aqueous stream with the electrolytic cell thereby creating an oxidized aqueous stream. At least a portion of the oxidized aqueous stream may be fed through a reverse osmosis membrane. The electrolytic cell may comprise at least two electrodes, wherein at least one electrode is a metal electrode, and a power source for powering the at least two electrodes.

The present invention provides an oxidant production apparatus, an example embodiment of which comprises a water container configured to accept and retain a volume of water; a porous salt container configured to accept and retain a quantity of salt, mounted with the water container such that salt in the salt container is in fluid communication with water in the water container; an electrolysis system mounted with the water container; and a gas directing element mounted with the salt container and the water container such that gas generated by the electrolysis system is preferentially directed through the salt container. In operation, gas from electrolysis percolates through the water and the salt, agitating the salt and encouraging the salt to fully dissolve.

The present disclosure describes methods and systems comprising hydrodynamic cavitation, microwave irradiation, and at least one of oxidative sonoelectrolysis and reductive sonoelectrolysis, providing feedstock purification of at least one of water, fluid and mineral. Contaminants, broken down and chemically degraded into smaller and more volatile substances by hydrodynamic cavitation are ultimately destroyed in the course of one or more sonoelectrolysis steps. In various embodiments, at least one of oxidative sonoelectrolysis and reductive sonoelectrolysis is irradiated with microwaves in order to heat the sonoplasma present within acoustic cavitation bubbles to temperatures sufficient to destroy contaminants therein.

Supercapacitive bioelectrical systems (SC-BESs) wherein the anode and cathode act as electrodes for a self-powered internal supercapacitor. The BES may further be enhanced by the use of optimized catalysts and enzymes to increase cell voltage and the use of a third capacitive electrode (AdE) short-circuited to the BES cathode and coupled to the BES anode to improve the power output of the self-powered internal supercapacitor.

Provided is an electrolysis apparatus with which the liquid that is to be treated can be continuously electrolyzed with high efficiency under high-temperature and high-pressure conditions. The electrolysis apparatus includes a cylindrical container main body including an inner peripheral surface serving as a cathode surface, an anode plate disposed in the container main body along an axis thereof, and end members attached to the respective ends of the container main body with nuts interposed therebetween, respectively. The end members are provided with nozzles, respectively, through which the liquid is passed. The end member is provided with a power supply rod connected to the anode plate which is inserted in the end member. Bipolar electrode plates are disposed in the container main body so as to be parallel to the anode plate. Insulators support the sides of the anode plate and the sides of the bipolar electrode plates.

A system and method for treating flowing water systems with a plasma discharge to remove or control growth of microbiological species. Components of the water system are protected from being damaged by excess energy from the electrohydraulic treatment. Ozone gas generated by a high voltage generator that powers the plasma discharge is recycled to further treat the water. A gas infusion system may be used to create fine bubbles of ozone, air, or other gases in the water being treated to aid in plasma generation, particularly when the conductivity of the water is high. An electrode mounting assembly maintains a high voltage electrode and ground electrode at a fixed distance from each other to optimize plasma generation. An open support structure for the high voltage generator circuit physically separates spark gap electrodes and resists metal deposits that may disrupt discharge of a high voltage pulse to create the plasma.

An electrode formed of synthetically produced, electrically conductive, doped diamond particles (2) embedded in a carrier layer (1) formed of electrically non-conductive material, wherein the diamond particles (2) protrude on both sides of the carrier layer (1) and come from a grain size range of 170 m to 420 m, wherein the diamond particles (2) in the electrode have grain sizes which differ from one another by at most 50 m.

At most 10% of the diamond particles (2) have a grain size outside the particular grain size range.