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CN108435193A - Reproducible removing organochlorine catalyst of one kind and preparation method thereof - Google Patents

Reproducible removing organochlorine catalyst of one kind and preparation method thereof Download PDF

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CN108435193A
CN108435193A CN201810325562.1A CN201810325562A CN108435193A CN 108435193 A CN108435193 A CN 108435193A CN 201810325562 A CN201810325562 A CN 201810325562A CN 108435193 A CN108435193 A CN 108435193A
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夏大寒
张先茂
王泽�
吴阳春
陈宗杰
王栋斌
周正
瞿玖
王瑜
王国兴
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Wuhan University of Technology WUT
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    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
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Abstract

本发明公开了一种可再生的脱除有机氯催化剂及其制备方法。该催化剂以铝源、硅源和镁源合成的复合氧化物为载体,以Ni、Mo、Cu、Ce为活性组分。按催化剂的质量百分比计,其活性组分中NiO含量为6.2‑15.6%,CuO含量为16.1‑25.4%,MoO3含量为1.7‑4.6%,CeO2含量为1.5‑2.5%,其余为载体;该催化剂以复合氧化物为载体,能较好的分散活性金属,具有有序孔道结构,特定孔径,孔容较大。能有效的脱除有机氯,避免后续的装置被无机氯腐蚀,提高油品的品质。同时该催化剂能持续再生,减少开停工时间,降低生产成本。The invention discloses a renewable catalyst for removing organic chlorine and a preparation method thereof. The catalyst uses composite oxide synthesized from aluminum source, silicon source and magnesium source as carrier, and Ni, Mo, Cu and Ce as active components. According to the mass percentage of the catalyst, the NiO content in the active component is 6.2-15.6%, the CuO content is 16.1-25.4%, the MoO content is 1.7-4.6%, the CeO content is 1.5-2.5%, and the rest are carriers; The catalyst uses a composite oxide as a carrier, can better disperse active metals, has an ordered pore structure, a specific pore diameter, and a large pore volume. It can effectively remove organic chlorine, prevent subsequent devices from being corroded by inorganic chlorine, and improve the quality of oil products. At the same time, the catalyst can be continuously regenerated, reducing the start-up and shutdown time and reducing the production cost.

Description

一种可再生的脱除有机氯催化剂及其制备方法A kind of renewable organic chlorine removal catalyst and preparation method thereof

技术领域technical field

本发明涉及一种可再生的用于脱除含氯石脑油中有机氯化物的催化剂及其制备方法,属于油品精制领域。The invention relates to a reproducible catalyst for removing organic chlorides in chlorinated naphtha and a preparation method thereof, belonging to the field of oil refining.

背景技术Background technique

在油田的开采后期,为了增加油田的产量,会使用一些含有机氯化物的助剂来增加采油率,导致部分原油中氯化物含量较高,含氯化合物主要富集在石脑油。石脑油中的氯化物主要是氯代烷烃,例如:三氯甲烷,二氯甲烷,三氯乙烷等。目前原油的脱盐工艺,只能脱除原油中的无机氯化物,不能脱除其中的有机氯化物。石脑油作为乙烯生产和催化重整的原料,石脑油中有机氯化物对设备不产生腐蚀,但是在进行预加氢过程中,有机氯在高温高压及氢气存在的条件下发生化学反应生产氯化氢,会腐蚀加氢系统下游设备。例如:腐蚀预加氢系统的空冷设备、水冷设备;氯化氢和加氢产生的氨反应生成氯化铵,堵塞管道;甚至进入预加氢循环氢压缩机的入口,严重影响循环氢压缩机的正常运转。为了防止有机氯在原油加工过程中转化为氯化氢造成设备的腐蚀,许多研究人员开发出多种类型的脱氯剂,有的脱氯剂已经工业应用多年。但是,这些脱氯剂主要集中在对馏分油中无机氯化物的脱除,针对有机氯的脱除的脱氯剂还鲜有报道。US5928500描述了一种脱除烃组分中微量有机氯化物的方法,该方法采用多孔性高比表面积的硅土做载体,Ni,Co或铁及其混合物的金属或金属氧化物为活性组分的吸附剂,将有机氯化物转化为金属氯化物从而将其脱除。CN200810049261专利中描述了一种脱除有机氯化物的吸附剂,这种吸附剂采用多孔性物质,诸如分子筛、氧化铝、活性炭为载体,浸渍金属氯化物或金属氯化物与金属硫酸盐的混合物。该吸附剂能够在含水的条件下将有机氯化物转化为无机氯化物,然后再用水洗的方法去除无机氯化物,这将增加脱氯精制步骤,造成工艺繁琐且还涉及到水洗后进一步脱除水分的问题。浸渍法虽然制备简易,但会造成吸附剂的表面积和孔容下降剧烈,从而影响动态吸附效果与床层寿命。US3864243公开了一种脱除烯烃组分中氯化物和其它杂质的方法,在室温、常压条件下,用孔径8A左右的13X或10X沸石分子筛可以将烃组分中氯化物吸附脱除。US20120190906专利中公开了分子筛的硅铝比对脱除有机氯容量的影响,结果表明硅铝比低于1.25的13X分子筛具有更高的有机氯吸附容量。13X分子筛虽然对有机氯具有一定的脱除效果,但总吸附容量有限且动态吸附速率低,使用寿命短。In the late stage of oilfield exploitation, in order to increase the output of the oilfield, some additives containing organic chlorides will be used to increase the oil recovery rate, resulting in high chloride content in some crude oil, and the chlorine-containing compounds are mainly enriched in naphtha. Chlorides in naphtha are mainly chlorinated alkanes, such as chloroform, dichloromethane, trichloroethane, etc. The current crude oil desalting process can only remove the inorganic chlorides in the crude oil, but cannot remove the organic chlorides. Naphtha is used as a raw material for ethylene production and catalytic reforming. The organic chlorides in naphtha do not cause corrosion to equipment, but during the pre-hydrogenation process, organic chlorine undergoes a chemical reaction under the conditions of high temperature, high pressure and the presence of hydrogen to produce Hydrogen chloride will corrode the downstream equipment of the hydrogenation system. For example: Corrosion of the air-cooling equipment and water-cooling equipment of the pre-hydrogenation system; hydrogen chloride reacts with the ammonia produced by hydrogenation to form ammonium chloride, which blocks the pipeline; even enters the inlet of the pre-hydrogenation cycle hydrogen compressor, seriously affecting the normal operation of the cycle hydrogen compressor run. In order to prevent the corrosion of equipment caused by the conversion of organic chlorine into hydrogen chloride during crude oil processing, many researchers have developed various types of dechlorination agents, and some dechlorination agents have been used in industry for many years. However, these dechlorination agents mainly focus on the removal of inorganic chlorides in distillate oils, and there are few reports on dechlorination agents aimed at the removal of organic chlorine. US5928500 describes a method for removing trace organic chlorides in hydrocarbon components. The method uses silica with high porosity and high specific surface area as a carrier, and metals or metal oxides of Ni, Co or iron and their mixtures as active components Adsorbents that convert organic chlorides to metal chlorides to remove them. CN200810049261 patent describes an adsorbent for removing organic chlorides. This adsorbent uses porous materials such as molecular sieves, alumina, and activated carbon as a carrier, impregnated with metal chlorides or a mixture of metal chlorides and metal sulfates. The adsorbent can convert organic chlorides into inorganic chlorides under water-containing conditions, and then remove inorganic chlorides by washing with water, which will increase the dechlorination refining steps, resulting in cumbersome processes and further removal after washing. moisture problem. Although the impregnation method is simple to prepare, it will cause a sharp decrease in the surface area and pore volume of the adsorbent, thereby affecting the dynamic adsorption effect and bed life. US3864243 discloses a method for removing chlorides and other impurities in olefin components. Under room temperature and normal pressure conditions, 13X or 10X zeolite molecular sieves with a pore size of about 8A can be used to remove chlorides in hydrocarbon components by adsorption. The US20120190906 patent discloses the influence of the silicon-aluminum ratio of molecular sieves on the removal capacity of organochlorine, and the results show that 13X molecular sieves with a silicon-aluminum ratio lower than 1.25 have higher organochlorine adsorption capacity. Although 13X molecular sieve has a certain removal effect on organic chlorine, its total adsorption capacity is limited, its dynamic adsorption rate is low, and its service life is short.

发明内容Contents of the invention

本发明主要针对石脑油中脱除有机氯的催化剂氯容低、不可再生等不足之处,开发出一种可再生的用于脱除含氯石脑油等油品中有机氯化物的催化剂。本发明提供了一种可再生的脱除有机氯的催化剂及其制备方法。本发明催化剂具有良好脱除有机氯性能,并可再生重复利用。The invention mainly aims at the shortcomings of the catalyst for removing organic chlorine in naphtha such as low chlorine capacity and non-renewability, and develops a regenerable catalyst for removing organic chlorides in oil products such as chlorinated naphtha . The invention provides a regenerable catalyst for removing organic chlorine and a preparation method thereof. The catalyst of the invention has good organic chlorine removal performance and can be regenerated and reused.

本发明催化剂是以铝源、硅源和镁源合成的复合氧化物为载体,以Ni、Mo、Cu、Ce为活性组分制得一种可再生的脱除有机氯催化剂。The catalyst of the invention uses the composite oxide synthesized from the aluminum source, the silicon source and the magnesium source as the carrier, and uses Ni, Mo, Cu and Ce as the active components to prepare a regenerable catalyst for removing organic chlorine.

所述的催化剂,其特征在于:所述的铝源、硅源和镁源合成的复合氧化物,按质量百分比计SiO2含量为3%~10%,MgO含量为9.2~18.9%,其余为Al2O3The catalyst is characterized in that: the composite oxide synthesized by the aluminum source, the silicon source and the magnesium source has a SiO content of 3% to 10% by mass percentage, a MgO content of 9.2 to 18.9%, and the rest are Al 2 O 3 .

所述催化剂活性组分含量以催化剂总质量计,其活性组分中NiO含量为6.2-15.6%,CuO含量为16.1-25.4%,MoO3含量为1.7-4.6%,CeO2含量为1.5-2.5%。The content of active components of the catalyst is based on the total mass of the catalyst, and the content of NiO in the active components is 6.2-15.6%, the content of CuO is 16.1-25.4%, the content of MoO3 is 1.7-4.6%, and the content of CeO2 is 1.5-2.5% %.

所述的催化剂,其特征在于:该催化剂的比表面积为430~526m2/g,孔容为0.85~1.1ml/g,孔径为4-10nm。The catalyst is characterized in that the specific surface area of the catalyst is 430-526m 2 /g, the pore volume is 0.85-1.1ml/g, and the pore diameter is 4-10nm.

所述的催化剂的制备方法,其特征在于:将一定量的铝源、硅源、镁源、可溶性的镍盐、表面活性剂和水混合均匀,得到初始溶胶凝胶混合物移入合成釜中密封,在150~220℃晶化8~24小时。将晶体浆液的pH值调节至中性,向反应釜中加入一定量的可溶性的钼盐、可溶性的铜盐和可溶性的铈盐,进行离子交换反应8~28h。待反应结束,将上述浆液加入絮凝剂沉淀、过滤、洗涤、干燥、挤条成型,过滤后液体回用用于下次反应。经100~150℃干燥2~4小时,500~700℃焙烧3~6小时后得到一种可再生的脱除有机氯催化剂。The preparation method of the catalyst is characterized in that: a certain amount of aluminum source, silicon source, magnesium source, soluble nickel salt, surfactant and water are uniformly mixed to obtain the initial sol-gel mixture and moved into a synthesis kettle for sealing, Crystallize at 150~220°C for 8~24 hours. Adjust the pH value of the crystal slurry to neutral, add a certain amount of soluble molybdenum salt, soluble copper salt and soluble cerium salt into the reaction kettle, and carry out ion exchange reaction for 8~28h. After the reaction is completed, the above slurry is added to a flocculant for precipitation, filtered, washed, dried, extruded, and the filtered liquid is reused for the next reaction. After drying at 100-150°C for 2-4 hours and roasting at 500-700°C for 3-6 hours, a regenerable organic chlorine removal catalyst is obtained.

按照本发明提供的催化剂,所述孔体积、比表面积、孔直径采用氮低温吸附法测定。According to the catalyst provided by the present invention, the pore volume, specific surface area and pore diameter are measured by a nitrogen low temperature adsorption method.

按照本发明提供的方法制备的一种可再生脱除有机氯催化剂适用于含有机氯的馏分油进行处理,能有效的脱除有机氯,生产含较低氯的馏分油。The regenerable organochlorine removal catalyst prepared according to the method provided by the invention is suitable for treating distillate oil containing organochlorine, can effectively remove organochlorine, and produce distillate oil containing lower chlorine.

本发明的上述技术方案与现有技术相比具有以下优点:Compared with the prior art, the above-mentioned technical solution of the present invention has the following advantages:

(1)本催化剂从分子结构设计的角度出发,制备出的催化剂具有有序孔道结构,特定孔径,孔容较大。利用催化剂低温吸附有机氯、高温转化脱附有机氯的性能,解决以往催化剂依靠单纯吸附脱除无机氯活性无法吸附有机氯的弊端,同时解决了有机氯吸附类催化剂氯容过低无法再生的问题。(1) From the perspective of molecular structure design, the prepared catalyst has an ordered pore structure, specific pore diameter, and large pore volume. Utilizing the properties of the catalyst for adsorbing organic chlorine at low temperature and converting and desorbing organic chlorine at high temperature, it solves the drawbacks of previous catalysts that rely on simple adsorption to remove inorganic chlorine activity and cannot adsorb organic chlorine, and at the same time solves the problem that the chlorine capacity of organic chlorine adsorption catalysts is too low and cannot be regenerated .

(2)硅酸镁、硅酸铝吸附剂对石脑油中的有机氯化物均有较好的吸附能力,两种物质可看做MgO·SiO2、Al2O3 .SiO2,即负载了金属氧化物的二氧化硅。在混合吸附剂中,氧化镁与氧化铝两种金属氧化物具有协同作用,增加了吸附剂的极性,从而提高了吸附剂对石脑油中氯化物的吸附能力。(2) Magnesium silicate and aluminum silicate adsorbents have good adsorption capacity for organic chlorides in naphtha, and the two substances can be regarded as MgO·SiO 2 , Al 2 O 3 .SiO 2 , that is, the loading Silicon dioxide with metal oxides. In the mixed adsorbent, the two metal oxides of magnesium oxide and aluminum oxide have a synergistic effect, which increases the polarity of the adsorbent, thereby improving the adsorption capacity of the adsorbent for chlorides in naphtha.

(3)Ce利于Ni-Mo-Cu等活性组分在载体表面上更好的分散,抑制晶粒的增长,催化剂的比表面积和孔容增大,氯容增加。在催化剂焙烧的过程中Ce3+氧化变价为Ce4+,而Ce4+具有更强的得电子能力,即L酸量增加,Ce改性催化剂的总酸量增加,能有效的抑制油品烯烃聚合,防止催化剂结焦,提高催化剂的抗结焦能力,延长催化剂的脱氯寿命。(3) Ce facilitates better dispersion of active components such as Ni-Mo-Cu on the surface of the carrier, inhibits the growth of grains, increases the specific surface area and pore volume of the catalyst, and increases the chlorine capacity. During the catalyst roasting process, Ce 3+ is oxidized to Ce 4+ , and Ce 4+ has a stronger ability to obtain electrons, that is, the amount of L acid increases, and the total acid amount of the Ce modified catalyst increases, which can effectively inhibit oil Olefin polymerization, prevent coking of the catalyst, improve the anti-coking ability of the catalyst, and prolong the dechlorination life of the catalyst.

(4)将环境友好型的镍-氨溶液作为模板剂使用,成功的将活性组分镍嵌入微孔催化剂前驱体中,为后续的Ni-Mo-Cu-Ce为活性组分催化剂的合成提供的保证。由于镍嵌入微孔中,在温度升高时能较好的保护镍原子,同时镍将吸附在催化剂上的活性氯激活,通过原子转移作用,让其从催化剂脱附;并且保证催化剂上的镍免于中毒,可再生循环使用。(4) The environment-friendly nickel-ammonia solution was used as a template, and the active component nickel was successfully embedded in the microporous catalyst precursor, which provided a basis for the subsequent synthesis of Ni-Mo-Cu-Ce as the active component catalyst. guarantee. Since the nickel is embedded in the micropores, it can better protect the nickel atoms when the temperature rises, and at the same time, the nickel activates the active chlorine adsorbed on the catalyst, and desorbs it from the catalyst through atom transfer; and ensures that the nickel on the catalyst Free from poisoning, renewable recycling.

具体实施实例:Specific implementation examples:

下面结合具体实施案例来详述本发明催化剂的特点、制备方法及其催化性能,但是本发明不仅限于这些例子,也不构成对发明实施范围的任何限定。The characteristics, preparation method and catalytic performance of the catalyst of the present invention will be described in detail below in conjunction with specific examples, but the present invention is not limited to these examples, nor does it constitute any limitation to the scope of the invention.

实施例1:Example 1:

将197g铝溶胶(Al2O3的含量22%)、33.3g硅溶胶(SiO2的含量30%)、38.1g硝酸镍、2.5g四乙基溴化铵和300g水,搅拌6h,混合均匀,得到初始溶胶凝胶混合物,初始溶胶凝胶物料移入合成釜中密封,在220℃晶化8小时。用0.5mol/L尿素将晶体浆液的pH值调节至中性,加入4.28g钼酸铵、59.7g硝酸铜和6.3g硝酸铈,进行离子交换反应8h。待反应结束,将上述浆液加入絮凝剂沉淀、过滤、洗涤、干燥、挤条成型,过滤后液体回用用于下次反应。经150℃干燥2小时,500℃焙烧6小时后得到可再生吸附脱氯催化剂Cat1。Mix 197g aluminum sol (Al 2 O 3 content 22%), 33.3g silica sol (SiO 2 content 30%), 38.1g nickel nitrate, 2.5g tetraethylammonium bromide and 300g water, stir for 6h, mix well , to obtain an initial sol-gel mixture, and the initial sol-gel material was moved into a synthesis kettle and sealed, and crystallized at 220° C. for 8 hours. The pH value of the crystal slurry was adjusted to neutral with 0.5mol/L urea, and 4.28g ammonium molybdate, 59.7g copper nitrate and 6.3g cerium nitrate were added, and the ion exchange reaction was carried out for 8h. After the reaction is completed, the above slurry is added to a flocculant for precipitation, filtered, washed, dried, extruded, and the filtered liquid is reused for the next reaction. After drying at 150°C for 2 hours and calcining at 500°C for 6 hours, a regenerable adsorption dechlorination catalyst Cat1 was obtained.

实施例2:Example 2:

将179g铝溶胶、10g硅溶胶、44.6g氯化镁、15.1g硝酸镍、2.5g十六烷基三甲基溴化铵和300g水,搅拌10h,混合均匀,得到初始溶胶凝胶混合物,初始溶胶凝胶物料移入合成釜中密封,在150晶化8小时。用0.5mol/L尿素将晶体浆液的pH值调节至中性,加入6.26g钼酸铵、59.7g硝酸铜和6.3g硝酸铈,进行离子交换反应28h。待反应结束,将上述浆液加入絮凝剂沉淀、过滤、洗涤、干燥、挤条成型,过滤后液体回用用于下次反应。经120℃干燥4小时,500℃焙烧6小时后得到可再生吸附脱氯催化剂Cat2。179g of aluminum sol, 10g of silica sol, 44.6g of magnesium chloride, 15.1g of nickel nitrate, 2.5g of cetyltrimethylammonium bromide and 300g of water were stirred for 10 hours and mixed evenly to obtain the initial sol-gel mixture, and the initial sol-gel The glue material was moved into a synthesis kettle and sealed, and crystallized at 150 for 8 hours. The pH value of the crystal slurry was adjusted to neutral with 0.5mol/L urea, and 6.26g of ammonium molybdate, 59.7g of copper nitrate and 6.3g of cerium nitrate were added, and the ion exchange reaction was carried out for 28h. After the reaction is completed, the above slurry is added to a flocculant for precipitation, filtered, washed, dried, extruded, and the filtered liquid is reused for the next reaction. After drying at 120°C for 4 hours and calcining at 500°C for 6 hours, a regenerable adsorption dechlorination catalyst Cat2 was obtained.

实施例3Example 3

将192.5g铝溶胶、23g硅溶胶、33g氯化镁、26.6g硝酸镍、2.5g四乙基溴化铵和300g水,搅拌6h,混合均匀,得到初始溶胶凝胶混合物,初始溶胶凝胶物料移入合成釜中密封,在220℃晶化20小时。用0.5mol/L尿素将晶体浆液的pH值调节至中性,加入4.28g钼酸铵、48.7g硝酸铜和5.1g硝酸铈,进行离子交换反应20h。待反应结束,将上述浆液加入絮凝剂沉淀、过滤、洗涤、干燥、挤条成型,过滤后液体回用用于下次反应。经120℃干燥3小时,600℃焙烧5小时后得到可再生吸附脱氯催化剂Cat3。192.5g of aluminum sol, 23g of silica sol, 33g of magnesium chloride, 26.6g of nickel nitrate, 2.5g of tetraethylammonium bromide and 300g of water were stirred for 6 hours and mixed evenly to obtain the initial sol-gel mixture, and the initial sol-gel material was transferred to the synthetic The kettle was sealed and crystallized at 220°C for 20 hours. Use 0.5mol/L urea to adjust the pH value of the crystal slurry to neutral, add 4.28g ammonium molybdate, 48.7g copper nitrate and 5.1g cerium nitrate, and carry out ion exchange reaction for 20h. After the reaction is completed, the above slurry is added to a flocculant for precipitation, filtered, washed, dried, extruded, and the filtered liquid is reused for the next reaction. After drying at 120°C for 3 hours and calcining at 600°C for 5 hours, a regenerable adsorption dechlorination catalyst Cat3 was obtained.

实施例4:Example 4:

将244g铝溶胶、23g硅溶胶、21.7g氯化镁、26.6g硝酸镍、2.5g十六烷基三甲基溴化铵和300g水,搅拌6h,混合均匀,得到初始溶胶凝胶混合物,初始溶胶凝胶物料移入合成釜中密封,在180℃晶化20小时。用0.5mol/L尿素将晶体浆液的pH值调节至中性,加入2.3g钼酸铵、37.8g硝酸铜和3.78g硝酸铈,进行离子交换反应28h。待反应结束,将上述浆液加入絮凝剂沉淀、过滤、洗涤、干燥、挤条成型,过滤后液体回用用于下次反应。经100℃干燥4小时,700℃焙烧3小时后得到可再生吸附脱氯催化剂Cat4。244g of aluminum sol, 23g of silica sol, 21.7g of magnesium chloride, 26.6g of nickel nitrate, 2.5g of cetyltrimethylammonium bromide and 300g of water were stirred for 6 hours and mixed evenly to obtain the initial sol-gel mixture, and the initial sol-gel The rubber material was transferred into a synthesis kettle and sealed, and crystallized at 180° C. for 20 hours. Adjust the pH value of the crystal slurry to neutral with 0.5mol/L urea, add 2.3g ammonium molybdate, 37.8g copper nitrate and 3.78g cerium nitrate, and carry out ion exchange reaction for 28h. After the reaction is completed, the above slurry is added to a flocculant for precipitation, filtered, washed, dried, extruded, and the filtered liquid is reused for the next reaction. After drying at 100°C for 4 hours and calcining at 700°C for 3 hours, a regenerable adsorption dechlorination catalyst Cat4 was obtained.

实施例5:Example 5:

本实施例对上述实施例1~4的脱氯催化剂和现有技术的催化剂Cat5活性对比测定。In this embodiment, the activities of the dechlorination catalysts of the above-mentioned Examples 1-4 and the catalyst Cat5 of the prior art are compared and measured.

对上述产品和焦化汽油脱硅催化剂的孔性质和酸性质进行分析,分析结果如表1The pore properties and acid properties of the above products and coker gasoline desiliconization catalyst were analyzed, and the analysis results are shown in Table 1

表1 不同催化剂的物化性质Table 1 Physicochemical properties of different catalysts

从表1可以看出本发明提供的催化剂Cat2~4载体中引入了MgO,相比未引入MgO的Cat1的具有更优的比表面积和孔容。本发明提供的催化剂Cat1~4通过特定的制备工艺,相比同等组成下的γ-Al2O3具有更大的孔径和孔容。It can be seen from Table 1 that MgO is introduced into the catalyst Cat2~4 carrier provided by the present invention, which has better specific surface area and pore volume than Cat1 without MgO. Catalysts Cat1-4 provided by the present invention have a larger pore diameter and pore volume than γ-Al 2 O 3 with the same composition through a specific preparation process.

将各实施例制备的催化剂分别取30ml装入Φ27×3.5mm的反应管,催化剂床层高度48mm,所用原料油为石脑油性质见表2。Take 30ml of the catalysts prepared in each embodiment and put them into a reaction tube of Φ27×3.5mm, the height of the catalyst bed is 48mm, and the raw material oil used is naphtha. The properties are shown in Table 2.

表2 石脑油性质Table 2 Properties of naphtha

项目project 密度,g/cm3 Density, g/ cm3 总氯,μg/gTotal chlorine, μg/g 石脑油naphtha 0.640.64 246246

选用分析仪: KY-200微库仑氯含量滴定仪测定油中有机氯。取30ml催化剂装入固定床反应器,进行器内活化,通入氢气,调整系统压力为0.7MPa,氢气量为50mL/min,以10℃/min升温至230℃,恒温2h,然后再以相同升温速率升温到400℃,恒温4h使催化剂完全活化。活化结束后,装置置换为氮气,泵入原料油石脑油,进油空速为1.5h-1,反应温度为150℃,反应压力为0.7MPa,氮气/油比100:1进行脱氯实验,脱氯后产品经水洗脱除无机氯后分析有机氯含量。待催化剂的脱氯效果下降后,将催化剂以10℃/min升温至250℃,反应压力提高至1.4 MPa,用氮气进行吹扫,待反应器出口气体检测氯含量为零,停止再生。反应温度降温至150℃,压力降至0.7MPa,重新进行脱氯实验。反应一定时间后取样分析,记录反应结果如表3所示。Selected analyzer: KY-200 microcoulomb chlorine content titrator to measure organic chlorine in oil. Take 30ml of catalyst and put it into a fixed bed reactor, activate the inside of the reactor, feed hydrogen, adjust the system pressure to 0.7MPa, the amount of hydrogen to 50mL/min, raise the temperature to 230°C at 10°C/min, keep the temperature for 2h, and then use the same The heating rate was raised to 400°C, and the temperature was kept constant for 4 hours to fully activate the catalyst. After the activation, the device was replaced with nitrogen, and the raw oil naphtha was pumped in. The oil inlet space velocity was 1.5h -1 , the reaction temperature was 150°C, the reaction pressure was 0.7MPa, and the nitrogen/oil ratio was 100:1 for dechlorination experiments. After dechlorination, the product is washed with water to remove inorganic chlorine, and then the organic chlorine content is analyzed. After the dechlorination effect of the catalyst decreases, the temperature of the catalyst is raised to 250°C at 10°C/min, the reaction pressure is increased to 1.4 MPa, and nitrogen is purged. When the chlorine content of the reactor outlet gas is detected to be zero, the regeneration is stopped. The reaction temperature was lowered to 150° C., the pressure was lowered to 0.7 MPa, and the dechlorination experiment was repeated. After reacting for a certain period of time, samples were taken and analyzed, and the reaction results were recorded as shown in Table 3.

表3 脱氯活性测定结果总氯,μg/gTable 3 Dechlorination activity test results total chlorine, μg/g

从表3的数据可知,Cat1,Cat2,Cat3,Cat4四种脱氯催化剂在石脑油有机氯含量约240μg/g原料中进行脱除有机氯实验,有机氯脱除达到97.9%以上,而对比催化剂Cat5在有机氯存在的的环境中脱除有机氯效果较差。为了进一步了解本发明催化剂的性能下面对催化剂Cat 3进行再生实验,实验结果见表3。实验结果表明:催化剂Cat3催化剂能有效的吸附脱除有机氯,并且能再生,重复使用。发明人还采用了上述方法对其他各实施例所得的催化剂进行了长周期实验,均能得到较好的结果,表明本发明催化剂具有较好的活性和稳定性。From the data in Table 3, it can be known that Cat1, Cat2, Cat3, and Cat4 four kinds of dechlorination catalysts were used in the experiment of removing organic chlorine in naphtha organic chlorine content of about 240 μg/g raw material, and the removal of organic chlorine reached more than 97.9%, while the comparison Catalyst Cat5 is less effective in removing organochlorine in the presence of organochlorine. In order to further understand the performance of the catalyst of the present invention, the regeneration experiment of catalyst Cat 3 is carried out below, and the experimental results are shown in Table 3. The experimental results show that the Cat3 catalyst can effectively absorb and remove organic chlorine, and can be regenerated and reused. The inventor also used the above method to carry out long-term experiments on the catalysts obtained in other examples, all of which obtained good results, indicating that the catalyst of the present invention has good activity and stability.

Claims (9)

1.一种可再生的脱除有机氯的催化剂,其特征在于:该催化剂是以铝源、硅源和镁源合成的复合氧化物为载体,以Ni、Mo、Cu、Ce为活性组分。1. A renewable catalyst for removing organochlorine, characterized in that: the catalyst is based on a composite oxide synthesized from an aluminum source, a silicon source and a magnesium source, with Ni, Mo, Cu, and Ce as active components . 2.按照权利要求1所述的催化剂,其特征在于:所述的复合氧化物载体,按质量百分比计SiO2含量为3%~10%,MgO含量为9.2~18.9%,其余为Al2O32. The catalyst according to claim 1, characterized in that: the composite oxide carrier has a SiO2 content of 3% to 10% by mass percentage, a MgO content of 9.2 to 18.9%, and the rest is Al2O 3 . 3.按照权利要求1所述的催化剂,其特征在于:所述的铝源为铝溶胶;硅源为硅溶胶;镁源为氯化镁。3. The catalyst according to claim 1, characterized in that: the aluminum source is aluminum sol; the silicon source is silica sol; the magnesium source is magnesium chloride. 4.根据权利要求1所述的催化剂,其特征在于:该催化剂的比表面积为430~526m2/g,孔容为0.85~1.1ml/g,孔径为4-10nm。4. The catalyst according to claim 1, characterized in that: the specific surface area of the catalyst is 430-526m 2 /g, the pore volume is 0.85-1.1ml/g, and the pore diameter is 4-10nm. 5.按照权利要求1所述的催化剂,其特征在于:催化剂活性组分含量以催化剂总质量计,其活性组分中NiO含量为6.2-15.6%,CuO含量为16.1-25.4%,MoO3含量为1.7-4.6%,CeO2含量为1.5-2.5%。5. according to the described catalyst of claim 1, it is characterized in that: catalyst active component content is based on catalyst gross mass, and in its active component, NiO content is 6.2-15.6%, CuO content is 16.1-25.4%, MoO Content 1.7-4.6%, CeO 2 content is 1.5-2.5%. 6.按照权利要求1~5任一项所述的催化剂的制备方法,其特征在于:一种可再生的脱除有机氯催化剂的制备方法如下:6. according to the preparation method of the described catalyst of any one of claim 1~5, it is characterized in that: a kind of preparation method of regenerable removal organochlorine catalyst is as follows: 将一定量的铝源、硅源、镁源、可溶性的镍盐、表面活性剂和水混合均匀,得到初始溶胶凝胶混合物移入合成釜中密封,在150~220℃晶化8~24小时;将晶体浆液的pH值调节至中性,向反应釜中加入一定量的可溶性的钼盐、可溶性的铜盐和可溶性的铈盐,进行离子交换反应8~28h;待反应结束,将上述浆液加入絮凝剂沉淀、过滤、洗涤、干燥、挤条成型,过滤后液体回用用于下次反应;经100~150℃干燥2~4小时,500~700℃焙烧3~6小时后得到一种可再生的脱除有机氯催化剂。Mix a certain amount of aluminum source, silicon source, magnesium source, soluble nickel salt, surfactant and water evenly to obtain the initial sol-gel mixture, move it into a synthesis kettle and seal it, and crystallize at 150~220°C for 8~24 hours; Adjust the pH value of the crystal slurry to neutral, add a certain amount of soluble molybdenum salt, soluble copper salt and soluble cerium salt to the reaction kettle, and carry out ion exchange reaction for 8~28h; after the reaction is completed, add the above slurry The flocculant is precipitated, filtered, washed, dried, extruded, and the filtered liquid is reused for the next reaction; dried at 100-150°C for 2-4 hours, and roasted at 500-700°C for 3-6 hours to obtain a Regenerated organochlorine removal catalyst. 7.根据权利要求6所述的催化剂的制备方法,其特征在于:所述的表面活性剂为四乙基溴化铵或十六烷基三甲基溴化铵。7. The preparation method of catalyst according to claim 6, characterized in that: the surfactant is tetraethylammonium bromide or cetyltrimethylammonium bromide. 8.根据权利要求6所述的催化剂的制备方法,其特征在于:用尿素将晶体浆液的pH值调节至中性。8. The preparation method of the catalyst according to claim 6, characterized in that: the pH value of the crystal slurry is adjusted to neutrality with urea. 9.根据权利要求6所述的催化剂的制备方法,其特征在于: 可溶性的钼盐、铜盐及铈盐为其铵盐或硝酸盐。9. The preparation method of the catalyst according to claim 6, characterized in that: the soluble molybdenum salt, copper salt and cerium salt are ammonium salts or nitrates.
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