Abstract: Disclosed are methods and devices that are useful for processing water-including waste such as wastewater and sludge by reacting the water-including waste with an amount of ferromagnetic powder, an amount of anionic flocullant and an amount of cationic flocullant forming ferromagnetic waste particles suspended in water of the fluid waste, the ferromagnetic waste particles subsequently separated from water of the fluid waste by application of a magnetic field.

Abstract: Disclosed are methods and devices that are useful for processing wastewater, such as stormwater runoff, greywater, blackwater and combinations thereof. In some embodiments of the devices, water is drawn from relatively deep in a microbial processing container, aerated with a Venturi air pump, and subsequently expelled to a relatively shallow part of the microbial processing container.

Abstract: Disclosed are methods and devices that are useful for processing water-including waste such as wastewater and sludge by reacting the water-including waste with an amount of ferromagnetic powder, an amount of anionic flocculant and an amount of cationic flocculant forming ferromagnetic waste particles suspended in water of the fluid waste, the ferromagnetic waste particles subsequently separated from water of the fluid waste by application of a magnetic field.

Abstract: Disclosed are methods and devices suitable for growing algae. In some embodiments, a device suitable for growing algae includes an algae growth-substrate assembly that comprises a pair of algae growth-substrates: an inwards-sloped substrate which directs liquid flowing on an upper surface thereof radially-inwards; and an outwards-sloped substrate which directs liquid flowing on an upper surface thereof radially-outwards, wherein the outwards-sloped substrate is located below and separated from the inwards-sloped substrate so that liquid from the inwards-sloped substrate falls onto the upper surface of the outwards-sloped substrate.

Abstract: Disclosed are methods and devices that are useful for processing water-including waste such as wastewater and sludge by reacting the water-including waste with an amount of ferromagnetic powder, an amount of anionic flocculant and an amount of cationic flocculant forming ferromagnetic waste particles suspended in water of the fluid waste, the ferromagnetic waste particles subsequently separated from water of the fluid waste by application of a magnetic field.

Abstract: Disclosed are methods and devices that are useful for processing wastewater, such as stormwater runoff, greywater, blackwater and combinations thereof. In some embodiments of the devices, water is drawn from relatively deep in a microbial processing container, aerated with a Venturi air pump, and subsequently expelled to a relatively shallow part of the microbial processing container.

Abstract: A method of preparing a fiberboard is described herein, the method comprising treating a particulate plant-derived material with plasma to obtain a plasma-treated particulate material, and compressing the plasma-treated particulate material. Further described herein is a fiberboard comprising a particulate plant-derived material, and being substantially devoid of an adhesive, or substantially devoid of an adhesive which is urea-formaldehyde resin, melamine-formaldehyde resin, polyurethane resin, epoxy resin, and/or phenol formaldehyde resin. The fiberboard may be characterized by a density of less than 500 kg/m3, a particulate plant-derived material particle area of at least 1 mm2, and/or a particulate plant-derived material water contact angle of no more than 20°.

Abstract: The present invention describes a method for manufacturing of a composite fixated material comprising the steps of: (a) providing bottom oil shale ash obtained after burning oil shale, said bottom oil shale (BOSA) comprises pozzolanic particles having size of about 10 to 4000 ?m and being capable of adsorbing trace elements at their surface; (b) providing acidic waste comprising said trace elements; and (c) adding the BOSA provided in step (a) to the acidic waste provided in step (b) in amount of about 0.1-0.4 weight parts of said BOSA per one weight part of said waste, and mixing said waste with said BOSA, thereby obtaining a neutralised (scrubbed) precipitate with the fixated trace elements, wherein said neutralised (scrubbed) precipitate with the fixated trace elements constitutes said composite fixated material.

Abstract: Disclosed are methods and devices suitable for growing algae.

Abstract: Disclosed are devices suitable for performing chemical and/or biological reactions. Also disclosed are methods of simultaneously performing at least two chemical and/or biological reactions under different conditions in a single reaction chamber.

Abstract: Disclosed are devices suitable for performing chemical and/or biological reactions. Also disclosed are methods of simultaneously performing at least two chemical and/or biological reactions under different conditions in a single reaction chamber.

Abstract: Disclosed are methods and devices suitable for growing algae.

Abstract: Disclosed are methods and devices useful for aerating and or adding additives to carbon-containing aqueous waste.

Abstract: Installation and method for processing wastewater, comprising: a) providing wastewater for processing; b) reducing O2 content of said wastewater by unactivated aerobic digestion; c) subsequently to ‘b’, eliminating substantially all O2 from said wastewater by anaerobic digestion; d) subsequently to ‘c’, transferring said wastewater to a closed photobioreactor; and e) subsequently to ‘d’, maintaining said wastewater in said photobioreactor in conditions favorable for algal photosynthesis, thereby allowing algae to grow in said photobioreactor. A method for growing algae is also disclosed whereby time, density and flow speed are controlled. The photobioreactor may have a conduit with two proportions of different cross sections.

Abstract: Disclosed are methods and devices suitable for growing algae.

Abstract: Aerator kit comprising a body defining a fluid-flow channel, and a nozzle insert disposed inside said body as such forming together a venturi aerator which is useful for aerating aqueous waste. The aerator can be used submerged as a part of an aerobic digester, in which gas or air flow into the nozzle inlet while drawing liquid through a peripheral hole in the aerators body and cause mixing. The aerator can be also used as an above ground aerator in which liquid is pumped into the nozzle inlet while drawing air through said peripheral hole. In an another embodiment the aerator could be also used for adding additive to a gas or liquid.

Abstract: Installation and method for processing wastewater, comprising: a) providing wastewater for processing; b) reducing O2 content of said wastewater by unactivated aerobic digestion; c) subsequently to ‘b’, eliminating substantially all O2 from said wastewater by anaerobic digestion; d) subsequently to ‘c’, transferring said wastewater to a closed photobioreactor; and e) subsequently to ‘d’, maintaining said wastewater in said photobioreactor in conditions favorable for algal photosynthesis, thereby allowing algae to grow in said photobioreactor. A method for growing algae is also disclosed whereby time, density and flow speed are controlled. The photobioreactor may have a conduit with two proportions of different cross sections.