KR20020010173A - A Method for Rejuvenating Hydrocarbon Conversion Catalyst - Google Patents
A Method for Rejuvenating Hydrocarbon Conversion Catalyst Download PDFInfo
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/04—Gas or vapour treating; Treating by using liquids vaporisable upon contacting spent catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/48—Liquid treating or treating in liquid phase, e.g. dissolved or suspended
- B01J38/60—Liquid treating or treating in liquid phase, e.g. dissolved or suspended using acids
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/48—Liquid treating or treating in liquid phase, e.g. dissolved or suspended
- B01J38/60—Liquid treating or treating in liquid phase, e.g. dissolved or suspended using acids
- B01J38/62—Liquid treating or treating in liquid phase, e.g. dissolved or suspended using acids organic
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/48—Liquid treating or treating in liquid phase, e.g. dissolved or suspended
- B01J38/68—Liquid treating or treating in liquid phase, e.g. dissolved or suspended including substantial dissolution or chemical precipitation of a catalyst component in the ultimate reconstitution of the catalyst
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Abstract
본 발명은 자력선별법으로 탄화수소 전환공정용 폐촉매에서 재생할 촉매를 분리하고, 이를 환경친화적인 방법으로 재생하는 방법에 관한 것이다. 본 발명의 탄화수소 전환공정용 폐촉매를 재생하는 방법은 자력선별법을 이용하여 탄화수소 전환공정용 폐촉매에서 재생할 촉매를 분리하는 공정; 분리된 촉매를 1 내지 20기압의 N2, He, Cl2, CCl4, CO, H2S, H2및 O2기체를 포함하는 그룹으로부터 선택되는 1종 이상의 기체로 포화시키고, 300 내지 1,000℃에서 30분 내지 6시간 동안 열처리하는 공정; 열처리된 촉매를 유기산, 무기산, 산화제 또는 환원제를 포함한 수용성 세척액으로 세척하는 공정; 및, 침전제 또는 전기적인 방법을 사용하여 세척액으로부터 금속을 회수하는 공정을 포함한다. 본 발명에 의하면, 자력선별법을 사용하여 경제적으로 재생할 수 있고, 유독가스를 거의 사용하지 않아 특수한 운전설비에 소요되는 비용이나 운전비용이 들지 않으며, 금속염화물, 염기 등을 포함한 유독폐수가 다량 발생하지 않는다. 또한, 세척액에서 금속회수가 용이하므로, 중금속함유 폐수가 발생하지 않을 뿐만 아니라, 세척액을 재사용할 수 있는 장점이 있다.The present invention relates to a method for separating a catalyst to be regenerated from a waste catalyst for hydrocarbon conversion process by magnetic screening, and regenerating it in an environmentally friendly method. The method for regenerating the spent catalyst for the hydrocarbon conversion process of the present invention comprises the steps of: separating the regenerated catalyst from the spent catalyst for the hydrocarbon conversion process using a magnetic screening method; The separated catalyst is saturated with one or more gases selected from the group comprising 1 to 20 atmospheres of N 2 , He, Cl 2 , CCl 4 , CO, H 2 S, H 2 and O 2 gases, and 300 to 1,000 Heat treatment at 30 ° C. for 30 minutes to 6 hours; Washing the heat treated catalyst with an aqueous washing solution containing an organic acid, an inorganic acid, an oxidizing agent or a reducing agent; And recovering the metal from the wash liquid using a precipitant or an electrical method. According to the present invention, it can be economically regenerated using the magnetic screening method, and it does not use any toxic gas, so it does not incur the cost or operating cost of a special operation facility, and does not generate a large amount of toxic wastewater including metal chlorides and bases. Do not. In addition, since the metal is easily recovered from the washing liquid, not only heavy metal-containing waste water is generated, but also the washing liquid can be reused.
Description
본 발명은 탄화수소 전환공정용 촉매의 재생방법에 관한 것이다. 좀 더 구체적으로, 본 발명은 자력선별법으로 탄화수소 전환공정용 폐촉매에서 재생할 촉매를 분리하고, 이를 환경친화적인 방법으로 재생하는 방법에 관한 것이다.The present invention relates to a method for regenerating a catalyst for a hydrocarbon conversion process. More specifically, the present invention relates to a method of separating a catalyst to be regenerated from a spent catalyst for hydrocarbon conversion process by magnetic screening, and recycling it in an environmentally friendly manner.
대표적인 탄화수소 전환공정인 휘발유를 생산하는 공정 중, 유동접촉식 촉매분해(FCC: fluid catalytic cracking), 잔사유 유동접촉식 촉매분해(RFCC: resid fluid catalytic cracking), 또는 탈황공정 등에는 대량의 촉매가 사용되고 있다. 이러한 공정에서 발생하는 다량의 폐촉매는 주로 매립이나 시멘트 등의 건설재료로 재활용되고 있으나, 전기 폐촉매를 재활용하는 가장 바람직한 방법은 폐촉매를 재생시켜서 다시 촉매로 활용하는 것이다.In the process of producing gasoline, a typical hydrocarbon conversion process, a large amount of catalyst is used in fluid catalytic cracking (FCC), resid fluid catalytic cracking (RFCC), or desulfurization. It is used. A large amount of waste catalyst generated in such a process is mainly recycled to construction materials such as landfill or cement, but the most preferable method of recycling the electric waste catalyst is to recycle the waste catalyst and use it as a catalyst again.
이러한 폐촉매를 재생하는 방법이 다각적으로 연구되고 있는데, 가장 일반적으로 사용되는 폐촉매의 재생방법은 폐촉매에 포함된 금속성분이 포함되어 사용이 불가능한 촉매입자와 금속성분이 포함되지 않거나 또는 소량의 금속성분을 포함하여 재사용이 가능한 촉매입자를 분리시키고, 재사용이 가능한 촉매입자를 다시 사용하는 것이다. 전기 분리를 위해 일반적으로 밀도를 이용한 부유선별과 포함된 금속들의 자기적인 성질을 이용한 자력선별이 사용된다. 이 중, 부유선별은 물 또는 용매를 사용하게 되므로 촉매를 처리하는 비용이 추가적으로 들고 단계가 복잡해지는 단점을 가지고 있으므로, 최근에는 자력선별법이 주로 이용되고 있다. 미국특허 제 4,406,773호에는 자력선별에 의해 폐촉매중에서 활성을 유지하고 있는 촉매부분을 분리하여 재사용이 가능하도록 하는 방법을 개시하고 있으나, 활성을 잃은 부분을 재생시키지는 못하므로, 완전한 폐촉매 처리기술을 제공하지 못한다는 단점이 있었다.Recycling of such spent catalysts has been studied in various ways. The most commonly used method of regenerating spent catalysts includes catalysts and metals that cannot be used because the metals contained in the spent catalysts are contained, Including the metal component to separate the reusable catalyst particles, and reuse the catalyst particles that can be reused. For electrical separation, flotation using density and magnetic separation using magnetic properties of the metals involved are commonly used. Among these, since the flotation uses water or a solvent, the cost of treating the catalyst is additionally increased, and the steps are complicated. In recent years, magnetic screening is mainly used. U. S. Patent No. 4,406, 773 discloses a method for separating and reusing a catalyst portion retaining activity in a spent catalyst by magnetic screening, but it does not regenerate the lost portion. There was a disadvantage that it can not provide.
한편, 활성을 잃은 부분에는 대부분 촉매에 금속이 침적되어 있으므로, 이 부분의 금속을 제거하여 촉매를 재생하려는 노력이 계속되어 왔다. 그러한 노력의 결과로, 촉매를 염소로 처리하여 금속염화물을 생성시켜 세척하는 염화법이 개발되었다. 전기 방법은 금속의 제거효율은 매우 뛰어나지만 유독한 염소기체를 사용하여 장치 및 운전하는 사람이 위험에 처할 수 있고, 염화물을 세척한 염소와 금속성분을 다량 함유한 폐수가 발생하며, 염소처리과정에서 촉매의 활성성분이 파괴될 수 있으므로 활성재생에도 민감한 조건을 요구하는 단점이 있었다.On the other hand, since most of the metal is deposited on the catalyst in the part where activity is lost, efforts have been made to regenerate the catalyst by removing the metal of this part. As a result of these efforts, a chloride process has been developed in which the catalyst is treated with chlorine to produce metal chlorides and washed. The electric method is very effective in removing metals, but the use of toxic chlorine gas can put the equipment and the operator at risk. Waste water containing a large amount of chlorine and metals washed with chloride is generated. In this case, the active ingredient of the catalyst can be destroyed, so it has a disadvantage of requiring a condition sensitive to active regeneration.
이에, 미국특허 제 4,267,032호에는 전처리로 소성과 황화수소처리를 하여 산화세척 및 환원세척의 두 가지 세척법을 이용하여, 금속제거율이 Ni 86 내지 92%(w/v), V 49 내지 51%(w/v) 및 Fe 53 내지 58%(w/v)인 금속제거방법이, 미국특허 제 4,686,197에는 소성한 폐촉매를 371℃에서 염화반응을 거쳐 물을 이용한 세척 과 산화세척 및 환원세척의 두 가지의 세척법을 이용하여 금속제거율이 Ni 70 내지 90%(w/v), V 50 내지 80%(w/v), Fe 30 내지 75%(w/v)인 금속제거방법이 각각 개시되었으며, 미국특허 제 5,155,073호에는 염화반응 전에 황화수소를 이용하여 촉매를 황화시켜서, Ni 95%(w/v), V 53%(w/v), Fe 77%(w/v)로 금속의 제거효율을 향상시킨 방법이 개시되었고, 일본특허 공개 (소)58-202049호에는 사염화탄소와 헥사클로로에탄을 사용한 염화법을 이용하여 금속제거율이 Ni 57%(w/v)인 방법이 개시되었는바, 전기 방법은 650 내지 800℃에서 소성을 거친 촉매를 그 온도에서 수소로 환원시켜 사염화탄소, 헥사클로로에탄을 기화시킨 기체에 300 내지 450℃에서 접촉시키고, 메탄올 또는 물을 이용하여 200℃ 10기압에서 세척하는 방법으로서, 조건에 따라서 바나디움(V)만을 선택적으로 제거할 수가 있었다.Thus, U.S. Patent No. 4,267,032 discloses a metal removal rate of Ni 86-92% (w / v), V 49-51% (by using two washing methods, oxidative washing and reducing washing, by pre-treatment and hydrogen sulfide treatment). w / v) and Fe 53-58% (w / v) metal removal method, US Pat. No. 4,686,197 discloses the fired waste catalyst through the chlorination reaction at 371 ℃ using water, oxidative washing and reduction washing Using a method of washing eggplant, a metal removal method having a metal removal rate of Ni 70 to 90% (w / v), V 50 to 80% (w / v) and Fe 30 to 75% (w / v) has been disclosed. , U. S. Patent No. 5,155, 073 discloses the removal efficiency of metals with Ni 95% (w / v), V 53% (w / v), Fe 77% (w / v) by sulfiding the catalyst with hydrogen sulfide prior to the chlorination reaction. Japanese Patent Application Laid-Open No. 58-202049 discloses a method in which the metal removal rate is 57% (w / v) using Ni chloride using carbon tetrachloride and hexachloroethane. As described above, the electric method is carried out by reducing the catalyst calcined at 650 to 800 ° C. with hydrogen at that temperature and contacting a gas of carbon tetrachloride, hexachloroethane at 300 to 450 ° C., and 200 ° C. using methanol or water. As a method of washing at 10 atmospheres, only vanadium (V) could be selectively removed depending on the conditions.
그러나, 전술한 재생방법들에는 세척액에 다량의 첨가제가 함유되어야만 하고, 이를 처리하는 공정이 복잡하며, 필연적으로 발생하는 중금속폐수에 대한 구체적인 처리방법이 기술되지 않아, 전기 방법들을 이용할 경우, 별도의 폐수처리장치를 설치하여야 하므로, 촉매의 재생시 필연적으로 발생하는 환경문제 및 이의 처리에 수반되는 비용이 신규생산 비용과 유사할 정도로 높아지는 단점이 있었다.However, the above-mentioned regeneration methods must contain a large amount of additives in the washing liquid, the process of treating them is complicated, and the specific treatment method for the heavy metal waste water generated inevitably is not described. Since the wastewater treatment apparatus has to be installed, there is a disadvantage in that the environmental problems inevitably generated during the regeneration of the catalyst and the costs associated with the treatment thereof are high enough to be similar to the new production costs.
따라서, 탄화수소 전환공정용 폐촉매를 환경친화적인 방법으로 재생하는 방법을 개발하여야 할 필요성이 끊임없이 대두되었다.Therefore, there is a constant need to develop a method for regenerating the waste catalyst for the hydrocarbon conversion process in an environmentally friendly manner.
이에, 본 발명자들은 탄화수소 전환공정용 폐촉매를 환경친화적인 방법으로 재생하는 기술을 확립하고자 예의 연구노력한 결과, 자력선별법으로 분리해 낸 촉매를 각종 기체로 포화된 조건하에 열처리하고, 이를 각종 유기산, 무기산, 산화제, 또는 환원제를 포함한 수용성 세척액으로 세척한 다음, 침전제 또는 전기적인 방법을 사용하여 세척액으로부터 금속을 회수하는 방법에 의해 탄화수소 전환공정용 촉매를 환경친화적으로 재생할 수 있음을 확인하고, 본 발명을 완성하게 되었다.Accordingly, the present inventors have made diligent efforts to establish a technology for regenerating the waste catalyst for hydrocarbon conversion process in an environmentally friendly manner, and heat treated the catalyst separated by the magnetic separation method under saturated gas and various organic acids, After washing with an aqueous washing liquid containing an inorganic acid, an oxidizing agent, or a reducing agent, and then recovering the metal from the washing liquid using a precipitant or an electrical method, it was confirmed that the catalyst for hydrocarbon conversion process can be environmentally regenerated. To complete.
결국, 본 발명의 주된 목적은 탄화수소 전환공정용 폐촉매를 재생하는 환경친화적인 방법을 제공하는 것이다.After all, the main object of the present invention is to provide an environmentally friendly method for regenerating spent catalyst for hydrocarbon conversion process.
도 1은 연속식 자력선별기를 이용한 폐촉매의 선별공정을 나타내는 모식도이다.1 is a schematic diagram showing a step of screening a waste catalyst using a continuous magnetic separator.
본 발명의 탄화수소 전환공정용 폐촉매를 재생하는 방법은 자력선별법을 이용하여 탄화수소 전환공정용 폐촉매에서 재생할 촉매를 분리하는 공정; 분리된 촉매를 1 내지 20기압의 N2, He, Cl2, CCl4, CO, H2S, H2및 O2기체를 포함하는 그룹으로부터 선택되는 1종 이상의 기체로 포화시키고, 300 내지 1,000℃에서 30분 내지6시간 동안 열처리하는 공정; 열처리된 촉매를 유기산, 무기산, 산화제 또는 환원제를 포함한 수용성 세척액으로 세척하는 공정; 및, 침전제 또는 전기적인 방법을 사용하여 세척액으로부터 금속을 회수하는 공정을 포함한다.The method for regenerating the spent catalyst for the hydrocarbon conversion process of the present invention comprises the steps of: separating the regenerated catalyst from the spent catalyst for the hydrocarbon conversion process using a magnetic screening method; The separated catalyst is saturated with one or more gases selected from the group comprising 1 to 20 atmospheres of N 2 , He, Cl 2 , CCl 4 , CO, H 2 S, H 2 and O 2 gases, and 300 to 1,000 Heat treatment at 30 ° C. for 30 minutes to 6 hours; Washing the heat treated catalyst with an aqueous washing solution containing an organic acid, an inorganic acid, an oxidizing agent or a reducing agent; And recovering the metal from the wash liquid using a precipitant or an electrical method.
이하, 본 발명의 탄화수소 전환공정용 폐촉매를 재생하는 방법을 공정별로 나누어 보다 구체적으로 설명하고자 한다.Hereinafter, the method for regenerating the spent catalyst for hydrocarbon conversion process of the present invention will be described in more detail by dividing the process.
제 1공정: 재생할 촉매의 분리 Step 1 : Separation of Regenerated Catalyst
자력선별법을 이용하여 탄화수소 전환공정용 폐촉매에서 재생할 촉매를 분리한다: 이때, 자력선별은 자력선별장치를 사용하여 수행되는데, 자력선별장치는 희토류 금속을 사용한 영구자석 또는 전자석을 사용하여 촉매를 분리하는 장치로서, 사용되는 자력은 바람직하게는 6,000 내지 50,000가우스, 보다 바람직하게는 8,000 내지 20,000가우스, 가장 바람직하게는 12,000가우스이고, 서스펜디드형, 드럼형, 격자형, 풀리형 등의 형태에 제한되지 않는다.The magnetic separation method is used to separate the regenerated catalyst from the spent catalyst for the hydrocarbon conversion process. The magnetic separation is performed by using a magnetic separation device, which uses a permanent or electromagnet using rare earth metal to separate the catalyst. The magnetic force used is preferably 6,000 to 50,000 gauss, more preferably 8,000 to 20,000 gauss, most preferably 12,000 gauss, and is not limited to forms such as suspended, drum, lattice, and pulleys. Do not.
제 2공정: 재생할 촉매의 열처리 Second Process : Heat Treatment of Regenerated Catalyst
분리된 촉매를 1 내지 20기압의 N2, He, Cl2, CCl4, CO, H2S, H2및 O2기체를포함하는 그룹으로부터 선택되는 1종 이상의 기체로 포화시키고, 300 내지 1,000℃에서 30분 내지 6시간 동안 열처리한다: 이때, 촉매에 따라 사용되는 기체는 단독 또는 2종 이상의 다른 기체와 혼합하여 사용할 수 있으며, 전기 기체를 기상에 포화시켜 사용할 수도 있으나, 기상에 함유된 전기 기체의 함량이 제한되는 것은 아니다. 전기 기체의 압력이 바람직하게는 1 내지 20기압, 좀 더 바람직하게는 7 내지 14기압, 가장 바람직하게는 10기압인 조건하에, 바람직하게는 300 내지 1,000℃, 보다 바람직하게는 500 내지 800℃, 가장 바람직하게는 650℃의 온도에서 바람직하게는 30분 내지 6시간, 보다 바람직하게는 1 내지 3시간, 가장 바람직하게는 2시간동안 열처리한다. 또한, 열처리된 촉매는 냉각시키지 않음이 바람직하나, 촉매에 따라 냉각시킬 수도 있다.The separated catalyst is saturated with one or more gases selected from the group comprising 1 to 20 atmospheres of N 2 , He, Cl 2 , CCl 4 , CO, H 2 S, H 2 and O 2 gases, and 300 to 1,000 Heat-treat at 30 ° C. for 30 minutes to 6 hours: At this time, the gas used according to the catalyst may be used alone or in admixture with two or more other gases, and may be used by saturating the electric gas in the gas phase, but in the gas phase The content of the gas is not limited. The pressure of the electric gas is preferably 1 to 20 atm, more preferably 7 to 14 atm, most preferably 10 atm, preferably 300 to 1,000 ° C, more preferably 500 to 800 ° C, Most preferably, the heat treatment is performed at a temperature of 650 ° C. for 30 minutes to 6 hours, more preferably 1 to 3 hours, and most preferably 2 hours. In addition, the heat treated catalyst is preferably not cooled, but may be cooled depending on the catalyst.
제 3공정: 열처리 촉매의 세척 3rd step : washing the heat treatment catalyst
열처리된 촉매를 유기산, 무기산, 산화제, 또는 환원제를 포함한 수용성 세척액으로 세척한다: 이때, 사용되는 유기산은 젖산, 초산, 숙신산, 옥살산, 구연산 등을 사용할 수 있고, 무기산은 HCl, HNO3, H2SO4. H3PO4등이 사용될 수 있으며, 산화제로는 H2O2또는O3가 사용될 수 있고, 환원제로는 SO2,금속황화물 등이 사용될 수 있다. 또한, 수용성 세척액은 전기 물질을 수용성 세척액에 대하여 0.01 내지 10%(w/v)로 포함하며, 함량이 1%(w/v)인 것이 특히 바람직하다. 수용성 세척액에포함되는 물질의 조성 및 혼합비는 특별히 제한되는 것은 아니나, 촉매의 종류에 따라 달라진다. 수용성 세척액의 온도는 15 내지 100℃가 바람직하나, 보다 바람직하게는 50 내지 80℃, 가장 바람직하게는 65℃로 유지하고, 이를 사용하여 세척할 때의 기상의 압력은 바람직하게는 1 내지 20기압, 보다 바람직하게는 1 내지 3기압, 가장 바람직하게는 1기압이다. 세척된 촉매는 건조된 후, 재사용된다.The heat treated catalyst is washed with an aqueous washing solution containing an organic acid, an inorganic acid, an oxidizing agent, or a reducing agent: wherein the organic acid used may be lactic acid, acetic acid, succinic acid, oxalic acid, citric acid, and the like, and the inorganic acid may be HCl, HNO 3 , H 2. SO 4 . H 3 PO 4 or the like may be used, H 2 O 2 or O 3 may be used as the oxidizing agent, SO 2, metal sulfide, or the like may be used as the reducing agent. In addition, the water-soluble washing liquid contains an electrical material of 0.01 to 10% (w / v) relative to the water-soluble washing liquid, it is particularly preferable that the content is 1% (w / v). The composition and the mixing ratio of the material contained in the aqueous washing solution are not particularly limited, but depend on the type of catalyst. The temperature of the water-soluble washing liquid is preferably 15 to 100 ° C, but more preferably 50 to 80 ° C, most preferably 65 ° C, and the pressure of the gas phase when washing with the water is preferably 1 to 20 atm. More preferably, it is 1-3 atmospheres, Most preferably, it is 1 atmosphere. The washed catalyst is dried and then reused.
제 4공정: 금속의 회수 Fourth Step : Recovery of Metal
침전제 또는 전기적인 방법을 사용하여 세척액으로부터 금속을 회수한다: 이때, 사용되는 침전제로는 Na2CO3, Na2SO4, NaHCO3, (NH4)2SO4, (NH4)2CO3등을 사용할 수 있으며, 전기적인 방법을 사용할 때는 사용된 세척액에 상온 상압에서 1 내지 100 V의 전압을 30분 내지 90분간 가하여 전극에 금속을 부착시켜서 금속을 회수한다The metal is recovered from the wash liquor using a precipitant or an electrical method: precipitants used are Na 2 CO 3 , Na 2 SO 4 , NaHCO 3 , (NH 4 ) 2 SO 4 , (NH 4 ) 2 CO 3 In the case of using the electric method, the metal is attached to the electrode by recovering the metal by applying a voltage of 1 to 100 V at a normal temperature and normal pressure for 30 minutes to 90 minutes.
이하, 실시예를 통하여 본 발명을 더욱 상세히 설명하고자 한다. 이들 실시예는 오로지 본 발명을 보다 구체적으로 설명하기 위한 것으로, 본 발명의 요지에 따라 본 발명의 범위가 이들 실시예에 의해 제한되지 않는다는 것은 당업계에서 통상의 지식을 가진 자에 있어서 자명할 것이다.Hereinafter, the present invention will be described in more detail with reference to Examples. These examples are only for illustrating the present invention in more detail, it will be apparent to those skilled in the art that the scope of the present invention is not limited by these examples in accordance with the gist of the present invention. .
실시예 1: 영구자석을 이용한 폐촉매의 분리 Example 1 Separation of Waste Catalyst Using Permanent Magnet
12,000가우스의 마그네틱 드럼형 영구자석을 이용한 연속식 자력선별기를 이용하여 평균적으로 Ni 6,200ppm, V 5,600ppm 및 Fe 3,600ppm의 금속을 함유하고, 잔사유 유동접촉식 촉매분해(RFCC: resid fluid catalytic cracking)공정에서 배출된 폐촉매 5kg을 분리하였다(참조: 도 1). 도 1에서, (1)은 자석으로 구성된 로울러를 나타내고, (2)는 벨트의 회전방향 및 자력의 방향을 나타내며, (3)은 벨트를 나타낸다. 폐촉매를 도 1과 같은 장치의 벨트에 도입하고, 자석으로 구성된 로울러를 회전시키면, 벨트에 도입된 폐촉매들이 낙하되게 되는데, 함유된 금속의 함량에 따라 자화도에 있어서 차이가 있는 폐촉매는 자화도에 따라, 낙하위치가 달라지게 된다. 이들을 크게 5개의 분획으로 분리한 결과, 가장 자화도가 높은 분획에는 금속함유량이 Ni 8,000ppm, V 6,200ppm 및 Fe 4,200ppm이며, 가장 자화도가 떨어지는 분획은 Ni 5,200ppm, V 5,200ppm 및 Fe 3,200ppm의 금속을 함유하고 있었다. 가장 자화도가 분획은 전체시료의 5%(w/v) 정도였으며, 가장 자화도가 떨어지는 분획은 전체의 60%(w/v)였다.Residual fluid catalytic cracking (RFCC) containing on average 6,200ppm, V 5,600ppm and Fe 3,600ppm metals using a continuous magnetic separator using 12,000 gauss magnetic drum-type permanent magnets 5 kg of the waste catalyst discharged from the process was separated (see FIG. 1). In Fig. 1, reference numeral 1 denotes a roller composed of a magnet, reference numeral 2 denotes a rotational direction of the belt and a direction of magnetic force, and reference numeral 3 denotes a belt. When the waste catalyst is introduced into the belt of the apparatus as shown in FIG. 1 and the roller formed of the magnet is rotated, the waste catalysts introduced into the belt fall. The waste catalyst having a difference in magnetization according to the amount of metal contained therein is Depending on the degree of magnetization, the drop position will vary. As a result of separating these into five fractions, the most highly magnetized fractions contained metals containing 8,000 ppm Ni, V 6,200 ppm and Fe 4,200 ppm. The fractions with the lowest magnetization were Ni 5,200 ppm, V 5,200 ppm and Fe 3,200. It contained ppm metal. The most susceptible fraction was about 5% (w / v) of all samples, and the least susceptible fraction was 60% (w / v).
실시예 2: 전자석을 이용한 폐촉매의 분리 Example 2 Separation of Waste Catalyst Using Electromagnet
마그네틱 드럼형 및 서스펜디드형의 전자석을 사용한 복합 자력선별기를 이용하여 폐촉매 5kg을 분리하였다. 실시예 1과 동일한 방법을 사용하여 모두 5개의분획으로 분리한 결과, 가장 자화도가 높은 분획에는 금속함유량이 Ni 8,200ppm, V 6,300ppm 및 Fe 4,400ppm이며, 가장 자화도가 떨어지는 분획은 Ni 4,500ppm, V 4,200ppm 및 Fe 2,800ppm의 금속을 함유하고 있었다. 실시예 1에 비하여, 자력이 높은 전자석장비를 사용하여 분리의 효율을 높일 수 있음을 알 수 있었다.5 kg of the waste catalyst was separated using a combination magnetic separator using a magnetic drum type and a suspended type electromagnet. Using the same method as in Example 1, all five fractions were used. As a result, the metals contained in the highest magnetization fraction had Ni 8,200 ppm, V 6,300 ppm and Fe 4,400 ppm, and the fraction having the lowest magnetization was Ni 4,500. It contained metals of ppm, V 4,200 ppm and Fe 2,800 ppm. Compared with Example 1, it was found that the efficiency of separation can be improved by using an electromagnet having a high magnetic force.
실시예 3: 분리된 촉매의 활성도 비교(Ⅰ) Example 3 Comparison of Activity of Separated Catalysts (Ⅰ)
실시예 2의 각 분획의 촉매활성도의 차이를 알아보기 위하여, 실시예 2에서 수득한 각 분획으로 미국표준검사법(American standard testing method: ASTM) D5154에 기술된 미세활성검사(micro activity test: MAT)를 실시하여, 그들의 탄화수소 전환활성도를 측정하고, 이들을 비교하였다. 자화도가 가장 높은 분획의 전환율은 76.2%였으며 수소의 수율은 0.8920%, 코크의 수율은 10.3420%임을 알 수 있었다. 또한, 가장 자화도가 낮은 분획의 전환율은 76.7%였으며, 수소의 수율은 0.3870%, 코크의 수율은 8.9218%임을 알 수 있었으므로, 금속의 함량이 줄어들어 생산물의 물성이 향상됨을 확인할 수 있었다.To determine the difference in catalytic activity of each fraction of Example 2, each fraction obtained in Example 2 was subjected to the micro activity test (MAT) described in the American standard testing method (ASTM) D5154. Was carried out to measure their hydrocarbon conversion activities and to compare them. The conversion rate of the highest magnetization fraction was 76.2%, and the yield of hydrogen was 0.8920% and the yield of coke was 10.3420%. In addition, the conversion rate of the fraction with the lowest magnetization was 76.7%, the yield of hydrogen was 0.3870%, the yield of coke was found to be 8.9218%, it was confirmed that the physical properties of the product is reduced by reducing the content of metal.
실시예 4: H2S기체를 이용한 폐촉매의 재생 Example 4 Regeneration of Spent Catalyst Using H 2 S Gas
실시예 2의 분획 중, 자화도가 가장 높은 부분 1kg을 금속을 제거하는 재생법을 사용하여 재생시켰다. 전기 폐촉매에 포함된 금속은 Ni 8,200ppm, V 6,500ppm, Fe 4,400ppm이었다.Of the fraction of Example 2, 1 kg of the highest magnetization part was regenerated using a regeneration method to remove metal. The metals included in the spent catalyst were Ni 8,200 ppm, V 6,500 ppm and Fe 4,400 ppm.
전기 폐촉매를 800oC에서 H2S기체 9.62%를 함유한 수소기체를 400ml/min으로 투입하며, 10기압에서 2시간 동안 열처리한 후, 상압에서 1%의 구연산 용액(w/v) 5L로 세척하였다. 세척된 촉매를 80oC에서 8시간 동안 건조시켜서 재생하였다. 재생된 촉매는 Ni 1,400ppm, V 3,200ppm 및 Fe 2,400ppm의 금속을 포함하고 있었다.Hydrogen gas containing 9.62% H 2 S gas at 400 ° C / min is charged at 800 o C, and heat treated at 10 atmospheres for 2 hours, followed by 5% of 1% citric acid solution (w / v) at atmospheric pressure. Washed with. The washed catalyst was regenerated by drying at 80 ° C. for 8 hours. The regenerated catalyst contained 1400 ppm Ni, 3200 ppm V and 2400 ppm Fe.
실시예 5: 산소를 이용한 폐촉매의 재생 Example 5 Regeneration of Spent Catalyst Using Oxygen
실시예 4에서 사용한 폐촉매를 700oC에서 산소로 포화되도록 산소기체를 400ml/min으로 투입하여 10기압을 유지하면서 3시간 동안 열처리한 후, 상압에서 0.05% HNO3용액(w/v) 5L로 세척하였다. 세척된 촉매는 80oC에서 8시간 동안 건조시켜서 재생하였다. 재생된 촉매는 Ni 7,800ppm, V 2,800ppm 및 Fe 4,100ppm의 금속을 포함하고 있었다.The waste catalyst used in Example 4 was heated to 400 ml / min to saturate with oxygen at 700 ° C., and then heat-treated for 3 hours while maintaining 10 atm, followed by 5 L of 0.05% HNO 3 solution (w / v) at atmospheric pressure. Washed with. The washed catalyst was regenerated by drying at 80 ° C. for 8 hours. The regenerated catalyst contained metals of Ni 7,800 ppm, V 2,800 ppm and Fe 4,100 ppm.
실시예 6: 분리된 촉매의 활성도 비교(Ⅱ) Example 6 Comparison of Activity of Separated Catalysts (II)
실시예 3의 방법으로 실시예 3 및 4의 재생된 촉매의 탄화수소 전환활성도를측정하고, 이들을 비교하였다. 실시예 3에서 재생된 촉매의 전환율은 81.1%, 수소의 수율은 0.1893% 및 코크의 수율은 9.1324%임을 알 수 있었다. 또한, 실시예 4에서 재생된 촉매의 전환율은 79.6%, 수소의 수율은 0.2238% 및 코크의 수율은 8.8724%임을 알 수 있었다.The hydrocarbon conversion activities of the regenerated catalysts of Examples 3 and 4 were measured by the method of Example 3 and these were compared. In Example 3, the conversion of the regenerated catalyst was 81.1%, the yield of hydrogen was 0.1893%, and the yield of coke was found to be 9.1324%. In addition, it was found that the conversion rate of the regenerated catalyst in Example 4 was 79.6%, the yield of hydrogen was 0.2238%, and the yield of coke was 8.8724%.
실시예 7: 침전제를 사용한 금속의 회수 Example 7 Recovery of Metal Using Precipitant
실시예 4에서 사용한 세척액에 포함된 금속성분들의 회수를 위하여 세척액 5L에 5g의 탄산나트륨을 첨가하여 침전시켰다. 세척액에 포함되어있는 금속성분은 Ni 78ppm, V 39ppm 및 Fe 51ppm이었다. 또한, Ni의 최대 침전 pH는 9.5, Fe의 최대 침전 pH는 6 및 V의 최대 침전 pH는 8.0이므로, 세척액의 pH를 조절하여 세척액에 녹아있는 Ni, Fe 및 V을 분리하였다. 각 해당하는 pH에서 침전된 금속탄산염을 필터로서 분리한 후, 세척액에는 Ni 7ppm, V 2ppm 및 Fe 3ppm의 금속성분이 잔류하였다.In order to recover the metal components included in the washing solution used in Example 4, 5 g of sodium carbonate was added to 5 L of the washing solution to precipitate. The metal components included in the washing solution were Ni 78 ppm, V 39 ppm and Fe 51 ppm. In addition, since the maximum precipitation pH of Ni is 9.5, the maximum precipitation pH of Fe is 6, and the maximum precipitation pH of 8.0 is 8.0, Ni, Fe, and V dissolved in the washing solution were separated by adjusting the pH of the washing solution. After separating the metal carbonate precipitated at each corresponding pH as a filter, a metal component of Ni 7ppm, V 2ppm and Fe 3ppm remained in the washing solution.
실시예 8: 전기적인 방법을 사용한 금속의 회수 Example 8 Recovery of Metal Using Electrical Method
실시예 5에서 사용한 세척액에 포함된 금속성분들의 회수를 위하여 전기적인 방법을 사용하였다. 세척액에 포함되어 있는 금속성분은 Ni 8ppm, V 42ppm 및 Fe 7ppm이었다. 양극과 음극의 탄소전극 2개를 사용하여, 세척액에 10V의 전압을 걸어주었다. 1시간 후에 탄소전극은 은백색으로 변하였고, 세척액에 포함되어 있는 금속성분은 Ni 3ppm, V 4ppm. Fe 2ppm이었다.An electrical method was used to recover the metal components included in the wash solution used in Example 5. Metal components included in the washing solution were Ni 8 ppm, V 42 ppm and Fe 7 ppm. A voltage of 10 V was applied to the cleaning liquid by using two carbon electrodes of the positive electrode and the negative electrode. After 1 hour, the carbon electrode turned silver white, and the metal components included in the cleaning solution were Ni 3 ppm and V 4 ppm. Fe was 2 ppm.
실시예 7 내지 8의 방법을 통하여, 특수한 설비없이 환경오염원이 될 수 있는 중금속을 손쉽게 순순분리하여 다른 공정에 이용할 수 있음은 물론, 세척액 내의 금속성분을 대부분 회수하였으므로, 세척액을 다시 사용할 수도 있음을 알게 되었다.Through the method of Examples 7 to 8, the heavy metal which can be an environmental pollutant without special equipment can be easily purely separated and used in other processes, and since most of the metal components in the washing liquid have been recovered, the washing liquid can be used again. I learned.
이상에서 상세히 설명하고 입증하였듯이, 본 발명은 자력선별법으로 탄화수소 전환공정용 폐촉매에서 촉매를 분리하고, 이를 각종 기체로 포화된 조건하에 열처리한 후, 각종 유기산, 무기산, 산화제, 또는 환원제를 포함한 수용성 세척액으로 세척한 다음, 침전제 또는 전기적인 방법을 사용하여 세척액으로부터 금속을 회수하는 환경친화적인 방법을 통하여 폐촉매를 재생하는 방법을 제공한다. 본 발명에 의하면, 자력선별법을 사용하여 경제적으로 재생할 수 있고, 유독가스를 거의 사용하지 않아 특수한 운전설비에 소요되는 비용이나 운전비용이 들지 않으며, 금속염화물, 염기 등을 포함한 유독폐수가 다량 발생하지 않는다. 또한, 세척액에서 금속회수가 용이하므로, 중금속함유 폐수가 발생하지 않을 뿐만 아니라, 세척액을 재사용할 수 있는 장점이 있다.As described and demonstrated in detail above, the present invention is to separate the catalyst from the spent catalyst for the hydrocarbon conversion process by magnetic separation method, and heat-treated it under conditions saturated with various gases, and then water-soluble including various organic acids, inorganic acids, oxidizing agents, or reducing agents. The present invention provides a method of regenerating a waste catalyst through an environmentally friendly method of washing with a washing liquid and then recovering metal from the washing liquid using a precipitant or an electrical method. According to the present invention, it can be economically regenerated using the magnetic screening method, and it does not use any toxic gas, so it does not incur the cost or operating cost of a special operation facility, and does not generate a large amount of toxic wastewater including metal chlorides and bases. Do not. In addition, since the metal is easily recovered from the washing liquid, not only heavy metal-containing waste water is generated, but also the washing liquid can be reused.
이상으로 본 발명 내용의 특정한 부분을 상세히 기술하였는 바, 당업계의 통상의 지식을 가진 자에게 있어서, 이러한 구체적 기술은 단지 바람직한 실시예일 뿐이며, 이에 의해 본 발명의 범위가 제한되는 것이 아닌 점은 명백할 것이다. 따라서, 본 발명의 실질적인 범위는 첨부된 청구항들과 그것들의 등가물에 의하여 정의된다고 할 것이다.As described above in detail specific parts of the present invention, it is apparent to those skilled in the art that such specific descriptions are merely preferred embodiments, and thus the scope of the present invention is not limited thereto. something to do. Thus, the substantial scope of the present invention will be defined by the appended claims and their equivalents.
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| CN119680654B (en) * | 2023-09-25 | 2025-11-18 | 中国石油天然气股份有限公司 | A method for preparing a low-cost slurry bed hydrogenation catalyst |
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