Abstract:
본 발명의 전기흡착식 수처리 장치는 하나 이상의 제1 유입구가 형성되어 유입수가 유입되는 외측판; 가장자리에 하나 이상의 제2 유입구가 형성되어 상기 유입수를 도입하는 내측판; 상기 외측판 및 내측판 사이에 형성되어 상기 유입된 유입수의 유로를 형성하는 다공성부재; 상기 내측판 상부에 하나 이상 적층되는 흡착셀; 및 상기 흡착셀 상부에 위치되고 하나 이상의 배출구가 형성되어 처리수가 유출되는 배출판;을 포함하는 것을 특징으로 한다.
Abstract:
PURPOSE: An exhaust gas treatment apparatus and a method for the same are provided to suppress the elution of iron ions and to reduce the oxidation of sulfur dioxide by preventing the corrosion of a catalytic module casing. CONSTITUTION: An exhaust gas treatment apparatus includes a catalytic reactor(10), a sacrificial anode, a lead wire(40). The catalytic reactor includes catalytic module casings(20, 22). The sacrificial anode is installed in a space of adjacent catalytic module casings. The lead wire electrically connects the catalytic module casings and the sacrificial anode. The catalyst is used for a selective catalyst reducing process for removing nitrogen oxide from exhaust gas. The catalytic module casings include iron.
Abstract:
PURPOSE: A selective catalytic reduction(SCR) catalyst regenerating method is provided to semi-permanently regenerate waste catalyst by washing the waste catalysts using an acid solution and carrying the washed catalyst in a zirconium-containing solution. CONSTITUTION: Waste catalysts are washed with an acid solution. The wasted catalysts are carried in a zirconium-containing solution. In an SCR catalyst, an active component containing a metal oxide is carried in a carrier. The carrier is one or more selected from titanium dioxide, alumina, and silica. The metal oxide is one or more selected from vanadium oxide, manganese oxide, barium oxide, molybdenum oxide, and tungsten oxide. The acid solution is one or more selected from sulfuric acid, nitric acid, hydrochloric acid, oxalic acid, and formic acid. The waste catalysts are further dried and fired.
Abstract:
A pre-treatment method of brucite for CO2 mineral carbonation is provided to effectively react unreacted brucite containing magnesium hydroxide with CO2 then generate carbonate by removing adsorbed water moiety, hydroxyl group and other volatile material in the brucite through the thermal treatment. The pre-treatment method includes steps of crushing brucite into granules with particle size of less than 125 micrometers possible to be heat treated(S10); homogeneously distributing the crushed granules to become thickness of less than 3cm(S20); and heat treating the processed granules at 400 to 1200deg.C for 10 minutes or more(S30). The pre-treatment method is carried out under atmosphere or a condition of introducing oxygen. As a result, various materials such as adsorbed water moiety, hydroxyl group and other volatile materials are removed from the unreacted brucite(Mg(OH)2).
Abstract:
PURPOSE: A vanadium pentoxide (V2O5) based catalyst for eliminating NOx contained in flue gas and preparation method thereof are provided to effectively convert nitrogen oxides to nitrogen gas even in the presence of excess sulfur dioxide gas by adding barium oxide (BaO) or calcium oxide (CaO) in the manufacturing process of the vanadium pentoxide based catalyst being supported on a honeycomb structure monolith made of titanium dioxide. CONSTITUTION: This vanadium pentoxide based catalyst is prepared by drying slurry-phase of an intermediate mainly comprising meta-titanic acid (TiO(OH)2) obtained in the manufacturing process of titanium dioxide (TiO2) for use in pigment; calcining at a temperature range of 400 to 700deg.C for at least 5 hours for preparing a honeycomb structure monolith made of titanium dioxide; supporting 1.0-10wt.% of vanadium pentoxide, 1-8wt.% of barium oxide (BaO) or calcium oxide (CaO) (based on the total weight of raw materials) on the honeycomb structure monolith.
Abstract:
PURPOSE: A regenerating method of a deactivated SCR catalyst is provided to simplify processes and to reduce chemical treatment cost. CONSTITUTION: A regenerating method of a deactivated SCR catalyst comprises a step of cleaning waste catalyst(S20) by using electrolyte oxidized water. The regenerating method of a deactivated SCR catalyst additionally comprises a step of washing a cleaned waste catalyst(S30), and a step of drying the waste catalyst(S40) before the cleaning step. The drying temperature is 150-250°C and the drying time is 1-3 hours. The regenerating method of a deactivated SCR catalyst additionally comprises a step of determining ORP[Oxidation Reduction Potential](S10), and a step of setting necessary cleaning time. [Reference numerals] (S10) Step of setting the ORP of electrolyte oxidized water; (S20) Step of cleaning with the electrolyte oxidized water; (S30) Step of washing; (S40) Step of drying
Abstract:
PURPOSE: A catalyst regeneration apparatus is provided to reduce the cost of more than a catalyst regeneration equipment line generating gradually and successively by performing a regeneration work on one chamber and reducing the moving cost of a catalyst to the place of the regeneration equipment by being movable. CONSTITUTION: A catalyst regeneration apparatus includes a chamber(110), a rotation part(120) accommodated in the chamber, a rotation driving part(130) installed in the chamber, an ultrasonic generator(150) installed in the chamber, and a control part(190). A chamber accommodates a catalyst and a regeneration solution improving the acidity of the catalyst. A rotation part separates a poisonous substance from the catalyst by rotating the catalyst. An ultrasonic generator generates an ultrasound and provides an ultrasound to a catalyst. A control part controls the rotation speed of the rotation part by controlling the rotation drive part. A poisonous substance discharging part(180) discharges a poisonous substance separated from the catalyst to the outside of the chamber. An acidity measuring part(160) measures the acidity of the generation solution in order to manage the acidity of the catalyst.
Abstract:
PURPOSE: A test reactor for evaluating a denitrification catalyst for exhaust gas is provided to rapidly and accurately evaluate the performance of the catalyst by using a binder including gypsum plaster. CONSTITUTION: A test reactor for evaluating a denitrification catalyst for exhaust gas comprises the following: a first insertion unit(103) for inserting reactants into a reactor pipe(203); an outside heater(205) supplying heat to the reactor pipe from the outside of the pipe; an inside heater supplying the heat to the reactor pipe from the inside of the pipe; a cooling unit(400) supplying cooling gas to the reactor pipe; a catalyst sample unit(300) filled with binders for fixing the catalyst; a thermocouple unit(204) for detecting the temperature of the catalyst; and a temperature controller(202).
Abstract:
A method of generating flue gas denitration waste catalyst is provided to determine cleaning time in the field by analyzing a state of the washing solution as a real time and not analyzing the washing solution in an analytical laboratory where analytical equipment is installed. A method of generating flue gas denitration waste catalyst comprises steps of: (S1) physically removing solid materials precipitated in the flue gas denitration waste catalyst; (S2) removing a poisoning substance precipitated in the flue gas denitration waste catalyst by washing the poisoning substance precipitated in the flue gas denitration waste catalyst by a washing solution for the cleaning time determined through measurement of hydrogen ion concentration; (S3) and drying the flue gas denitration waste catalyst.