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High viscosity material odor treatment process and catalyst manufacturing method using the electric dust collector and a catalyst ozone process

机译:使用电集尘器和催化剂臭氧工艺的高粘度材料气味处理工艺和催化剂制造方法

摘要

The present invention relates to an exhaust gas recirculation system for an exhaust gas recirculation system for an exhaust gas recirculation system for an exhaust gas recirculation system, An electric dust collector for recovering oil mist and organic solvents by an electric dust collection method by a corona discharge, and a residual odor remover for removing residual odor remaining in the exhaust gas separated from the oil mist and the organic solvent due to the electrostatic precipitator through the catalyst ozone And a discharging means for discharging the exhaust gas from which the odor has been removed by the residual odor removing means to the outside by using a blower, and a process for treating the high viscous odor material using catalytic ozone oxidation, A first step of moving the exhaust gas to a heat exchanger; A second step of allowing the heat exchanger to cool the exhaust gas that is moved from the inlet pipe and flows in; A third step of recovering the oil mist and the organic solvents contained in the exhaust gas cooled and moved by the heat exchanger by an electrostatic precipitator; A fourth step of removing the remaining odor remaining in the exhaust gas from which the organic solvents have been recovered by the electrostatic precipitator through the residual odor removing means; And a fifth step of discharging the exhaust gas from which the odor is removed by the residual odor removing means to the outside through the discharging means. Further, the present invention provides a method for preparing a catalyst for removing residual odor in a process for treating a high-viscous odorous substance using the above-described electrostatic precipitator and catalytic ozone oxidation, comprising the steps of: dissolving potassium permanganate (KMnO 4 ) in water at 50 ° C; It was dissolved in ammonium bicarbonate (NH 4 HCO 3) in the melting stage water temperature raising step of raising the temperature to 65 ℃; A precipitate first precipitate forming step of forming a precipitate of manganese dioxide (MnO 2 ) in the water in which potassium permanganate (KMnO 4 ) and ammonium bicarbonate (NH 4 HCO 3 ) are dissolved; Cooling the precipitated manganese dioxide (MnO 2 ) to room temperature; Adjusting the pH of the aqueous solution to 3 using sulfuric acid (H 2 SO 4 ) to remove the ammonia of the precipitated manganese dioxide (MnO 2 ) by the cooling step; Forming a precipitate of Cu (OH) 2 CuCO 3 by adding a copper sulfate (II) acetic acid (CuSO 4 - 5 H 2 O) and ammonium bicarbonate (NH 4 HCO 3 ) after the adjustment; Rinsing several times with distilled water to remove SO 42- remaining in the Cu (OH) 2 CuCO 3 precipitate; Drying the Cu (OH) 2 CuCO 3 precipitate after the step of rinsing (S700), and molding the pellet into a pellet of a predetermined size by a pressure molding extruder.
机译:本发明涉及用于废气再循环系统的废气再循环系统的废气再循环系统的废气再循环系统,通过电晕放电通过电集尘方法回收油雾和有机溶剂的电集尘器。以及通过除臭剂去除通过静电除尘器从油雾和有机溶剂中分离出的废气中残留的残留气味的残留气味去除剂,以及通过该装置排出已去除了气味的废气的排放装置。使用鼓风机将残留的异味去除装置排到外部,以及利用催化臭氧氧化处理高粘度异味材料的方法,第一步骤是将废气移动到热交换器中;第二步骤是使热交换器冷却从进气管流入并流入的废气。第三步,用静电除尘器回收由热交换器冷却和移动的废气中所含的油雾和有机溶剂。第四步骤是通过静电除尘器除去残留在废气中的残留异味,其中该残留异味已通过静电除尘器从其中回收了有机溶剂;以及第五步骤,将通过残留气味去除装置去除了气味的废气通过排放装置排放到外部。此外,本发明提供了一种在使用上述静电除尘器和臭氧催化氧化法处理高粘性气味物质的方法中制备用于去除残留气味的催化剂的方法,该方法包括以下步骤:溶解高锰酸钾(KMnO < Sub> 4 )在50°C的水中;在升温至65℃的熔融阶段水温升高步骤中,将其溶于碳酸氢铵(NH 4 HCO 3)中。沉淀物第一沉淀物形成步骤,在水中形成高锰酸钾(KMnO 4 )和碳酸氢铵(NH )的二氧化锰(MnO 2 )沉淀物。 4 HCO 3 )溶解;将沉淀的二氧化锰(MnO 2 )冷却至室温;使用硫酸(H 2 SO 4 )调节水溶液的pH值至3,以去除沉淀的二氧化锰(MnO 2 )通过冷却步骤;通过添加硫酸铜(II)乙酸(CuSO 4-5 H 2 CuCO 3 形成沉淀> 2 O)和碳酸氢铵(NH 4 HCO 3 );用蒸馏水漂洗几次以除去残留在Cu(OH) 2 CuCO 3 中的SO 4 2-沉淀;在漂洗步骤(S700)之后,干燥Cu(OH)2,Sub 2,Cu 3 Sub的沉淀物,并通过压力成型挤出机将所述颗粒成型为预定尺寸的颗粒。

著录项

  • 公开/公告号KR101912595B1

    专利类型

  • 公开/公告日2019-01-14

    原文格式PDF

  • 申请/专利权人 주식회사 지이테크;

    申请/专利号KR20160109803

  • 发明设计人 조윤현;

    申请日2016-08-29

  • 分类号B03C3/38;A61L9/01;A61L9/16;B03C3/32;

  • 国家 KR

  • 入库时间 2022-08-21 11:49:26

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