A water treatment apparatus includes: a treatment tank, having therein a grounded electrode and a high-voltage electrode opposing the grounded electrode, for generating electric discharge between both the electrodes, and causing to-be-treated water to pass between the electrodes and contact with the electric discharge to perform water treatment, an ozone mixing portion for supplying ozone-containing gas in the treatment tank through a gas sending portion to the to-be-treated water supplied from outside, and a gas returning portion for sending gas in the ozone mixing portion to the treatment tank, are provided, and water treatment is performed by ozone in the ozone mixing portion, and water treatment is thereafter performed by the electric discharge in the treatment tank.

A water treatment apparatus includes: a treatment tank, having therein a grounded electrode and a high-voltage electrode opposing the grounded electrode, for generating electric discharge between both the electrodes, and causing to-be-treated water to pass between the electrodes and contact with the electric discharge to perform water treatment, an ozone mixing portion for supplying ozone-containing gas in the treatment tank through a gas sending portion to the to-be-treated water supplied from outside, and a gas returning portion for sending gas in the ozone mixing portion to the treatment tank, are provided, and water treatment is performed by ozone in the ozone mixing portion, and water treatment is thereafter performed by the electric discharge in the treatment tank.

A method of treating water containing arsenic and manganese. Ozone is injected into the water at a concentration in the range of 0.2 to 1.0 mg/L, oxidizing As(III) to As(V) and Mn(II) to Mn(IV). Ferric chloride coagulant is added to the ozonated water, coagulating the As(V) and the Mn(IV). The water is then filtered with a first filter medium selected for removal of the Mn(IV) followed by a second filter medium selected for removal of As(V). This removes the coagulate to produce treated water. The method removes arsenic and manganese to low levels acceptable for drinking water, using low concentrations of ozone as an oxidant. An advantage is that the ozone system can have a relatively small footprint, and use less energy, an important factor for climate change. Further, a quenching agent for removal of residual ozone is not required.

A method of treating water containing arsenic and manganese. Ozone is injected into the water at a concentration in the range of 0.2 to 1.0 mg/L, oxidizing As(III) to As(V) and Mn(II) to Mn(IV). Ferric chloride coagulant is added to the ozonated water, coagulating the As(V) and the Mn(IV). The water is then filtered with a first filter medium selected for removal of the Mn(IV) followed by a second filter medium selected for removal of As(V). This removes the coagulate to produce treated water. The method removes arsenic and manganese to low levels acceptable for drinking water, using low concentrations of ozone as an oxidant. An advantage is that the ozone system can have a relatively small footprint, and use less energy, an important factor for climate change. Further, a quenching agent for removal of residual ozone is not required.

This invention relates to a method for producing geothermal power using geothermal brines while producing a reduced silica and iron brine having improved injectivity. The resulting compositions include a composition with reduced silica, iron, and lithium having reduced quantity of total suspended solids.

This invention relates to a method for producing geothermal power using geothermal brines while producing a reduced silica and iron brine having improved injectivity. The resulting compositions include a composition with reduced silica, iron, and lithium having reduced quantity of total suspended solids.

A method of treating water containing arsenic and manganese. Ozone is injected into the water at a concentration in the range of 0.2 to 1.0 mg/L, oxidizing As(III) to As(V) and Mn(II) to Mn(IV). Ferric chloride coagulant is added to the ozonated water, coagulating the As(V) and the Mn(IV). The water is then filtered with a first filter medium selected for removal of the Mn(IV) followed by a second filter medium selected for removal of As(V). This removes the coagulate to produce treated water. The method removes arsenic and manganese to low levels acceptable for drinking water, using low concentrations of ozone as an oxidant. An advantage is that the ozone system can have a relatively small footprint, and use less energy, an important factor for climate change. Further, a quenching agent for removal of residual ozone is not required.

A method of treating water containing arsenic and manganese. Ozone is injected into the water at a concentration in the range of 0.2 to 1.0 mg/L, oxidizing As(III) to As(V) and Mn(II) to Mn(IV). Ferric chloride coagulant is added to the ozonated water, coagulating the As(V) and the Mn(IV). The water is then filtered with a first filter medium selected for removal of the Mn(IV) followed by a second filter medium selected for removal of As(V). This removes the coagulate to produce treated water. The method removes arsenic and manganese to low levels acceptable for drinking water, using low concentrations of ozone as an oxidant. An advantage is that the ozone system can have a relatively small footprint, and use less energy, an important factor for climate change. Further, a quenching agent for removal of residual ozone is not required.

The present invention discloses a high-purity separation method of iron ions from an aqueous solution containing heavy metal ions, wherein after pretreatment of an aqueous solution containing heavy metal ions, sedimentation containing iron ions are collected, nitric acid or sulfuric acid is added for dissolution, and then a reducing agent is added to the dissolved solution; and after heating and sealing reaction, red sedimentation is generated at the bottom, The sedimentation has a high purity, and the residual amount of iron in the solution is less than 0.4 mg/L. In the method, iron ions in the solution can be converted to hematite crystals at a high purity, and the solution has an excellent retention rate of heavy metal ions, the reaction time is short, the separation efficiency is high, the operation is simple, and the cost is low.

The present invention discloses a high-purity separation method of iron ions from an aqueous solution containing heavy metal ions, wherein after pretreatment of an aqueous solution containing heavy metal ions, sedimentation containing iron ions are collected, nitric acid or sulfuric acid is added for dissolution, and then a reducing agent is added to the dissolved solution; and after heating and sealing reaction, red sedimentation is generated at the bottom, The sedimentation has a high purity, and the residual amount of iron in the solution is less than 0.4 mg/L. In the method, iron ions in the solution can be converted to hematite crystals at a high purity, and the solution has an excellent retention rate of heavy metal ions, the reaction time is short, the separation efficiency is high, the operation is simple, and the cost is low.