CN110394152A - A kind of preparation method and product of selective separation palladium ion adsorption material - Google Patents
A kind of preparation method and product of selective separation palladium ion adsorption material Download PDFInfo
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Abstract
Description
技术领域technical field
本发明属于钯离子分离回收利用领域,具体涉及一种选择性分离钯离子吸附材料的制备方法及产品。The invention belongs to the field of separation, recovery and utilization of palladium ions, and in particular relates to a preparation method and a product of an adsorption material for selectively separating palladium ions.
背景技术Background technique
含钯废液的主要来源是各电子行业工艺生产中活化、钝化等电镀废液,该废液呈弱酸性,钯含量为~50ppm。钯金、黄金等贵金属生产的废液中含有~10ppm的钯。印刷电路板孔金属化、塑料电镀及各种非金属电镀活化后的工件清洗废水也含有一定量的钯,其含量为~1ppm。研究发现,电镀行业中大量含钯废液当做普通废水处理排放,不仅加大了后续废水处理的难度,而且造成了资源的浪费。据统计,我国电镀及电路板行业每年产生的含钯废液中有3吨左右的金属钯不能得到有效回收。此外,钯排放积累于环境中会危害人类健康,如引起哮喘、过敏和鼻炎等疾病。为了提高印刷电路板废液中钯的回收率,国内外研究者先后对萃取法、离子交换法以及树脂吸附法等技术进行了不同程度的研究。虽然这些研究在某些方面取得了一定的进展,但也都存在一定的不足,较好的处理技术也仅能使钯含量降低至3~4ppm。含钯废液中钯呈不同的形态是导致钯回收率降低的重要原因之一。The main source of palladium-containing waste liquid is electroplating waste liquid such as activation and passivation in the process production of various electronic industries. The waste liquid is weakly acidic and the palladium content is ~50ppm. Palladium, gold and other precious metal production waste liquid contains ~ 10ppm of palladium. The workpiece cleaning wastewater after the metallization of printed circuit board holes, plastic electroplating and various non-metallic electroplating activation also contains a certain amount of palladium, and its content is ~ 1ppm. The study found that a large amount of palladium-containing waste liquid in the electroplating industry is discharged as ordinary wastewater, which not only increases the difficulty of subsequent wastewater treatment, but also causes a waste of resources. According to statistics, about 3 tons of metal palladium in the palladium-containing waste liquid produced by my country's electroplating and circuit board industries cannot be effectively recovered. In addition, the accumulation of palladium emissions in the environment will endanger human health, such as causing diseases such as asthma, allergies and rhinitis. In order to improve the recovery rate of palladium in printed circuit board waste liquid, researchers at home and abroad have successively carried out different researches on technologies such as extraction method, ion exchange method and resin adsorption method. Although these studies have made some progress in some aspects, there are still some shortcomings. Better treatment technology can only reduce the palladium content to 3-4ppm. The different forms of palladium in palladium-containing waste liquid is one of the important reasons for the decrease of palladium recovery.
现有工艺也合成了一些用于吸附分离钯的复合材料,但是使用效果有限。比如CN102009983A公开了一种巯基改性SBA-15分子筛及其制备和使用方法,其利用将SBA-15分子筛加入所配制的巯基改性剂乙醇水溶液中,常温搅拌36~48h,获得巯基改性SBA-15分子筛产物。其使用乙醇作为介质,并且反应时间过长,最后的产品效率也不令人满意。CN1136960C公开了一种制备巯基官能化MCM-48介孔分子筛的方法。其利用MCM-48介孔分子筛与巯丙基三甲氧基硅烷甲苯溶液回流12~24小时制备,但是其采用介孔分子筛与巯丙基三甲氧基硅烷甲苯溶液直接回流的反应方式,制备得到的产品吸附效果有限。CN201510379076.4公开了一种端羧基树枝状聚合物吸附材料及其制备方法,其公开的技术方案为将三聚氰氯溶于丙酮或四氢呋喃中,加入到二元醇的丙酮溶液中,制得一代端羟基树枝状聚合物粗品,提纯得一代端羟基树枝状聚合物;以三聚氰氯为核,一代端羟基树枝状聚合物为支化单元,制得二代、三代端羟基树枝状聚合物粗品,再提纯;将端羟基树枝状聚合物分散于水中,加入马来酸酐和对甲苯磺酸,制得端羧基树枝状聚合物粗品,提纯得到端羧基树枝状聚合物吸附材料。此专利运用了羧基吸附特性,但是其公开的技术方案全利用高分子材料,成本高,工艺条件复杂。Some composite materials for adsorption and separation of palladium have also been synthesized in the existing technology, but the use effect is limited. For example, CN102009983A discloses a mercapto-modified SBA-15 molecular sieve and its preparation and use method. It utilizes adding SBA-15 molecular sieve into the prepared mercapto-modifier ethanol aqueous solution and stirring at room temperature for 36-48 hours to obtain mercapto-modified SBA -15 molecular sieve product. It uses ethanol as a medium, and the reaction time is too long, and the final product efficiency is also unsatisfactory. CN1136960C discloses a method for preparing sulfhydryl functionalized MCM-48 mesoporous molecular sieve. It is prepared by using MCM-48 mesoporous molecular sieve and mercaptopropyltrimethoxysilane toluene solution to reflux for 12 to 24 hours, but it adopts the reaction method of direct reflux of mesoporous molecular sieve and mercaptopropyltrimethoxysilane toluene solution to prepare the Product adsorption is limited. CN201510379076.4 discloses a carboxyl-terminated dendritic polymer adsorption material and a preparation method thereof. The disclosed technical scheme is to dissolve cyanuric chloride in acetone or tetrahydrofuran and add it to the acetone solution of dibasic alcohols to obtain The crude product of the first-generation hydroxyl-terminated dendritic polymer is purified to obtain the first-generation hydroxyl-terminated dendritic polymer; the second-generation and third-generation hydroxyl-terminated dendritic polymers are obtained by using cyanuric chloride as the core and the first-generation hydroxyl-terminated dendritic polymer as the branch unit The crude product is purified again; the hydroxyl-terminated dendritic polymer is dispersed in water, and maleic anhydride and p-toluenesulfonic acid are added to obtain a crude carboxyl-terminated dendritic polymer, which is purified to obtain a carboxyl-terminated dendritic polymer adsorption material. This patent utilizes carboxyl adsorption properties, but its disclosed technical solutions all use polymer materials, which have high cost and complicated process conditions.
发明内容Contents of the invention
有鉴于此,本发明目的在于提供一种选择性分离钯离子吸附材料的制备方法及产品,本发明通过将硅胶与氧化石墨烯进行结合,并进一步通过化学接枝的方法将复合材料表面引入双键和巯基,然后将材料进行钯离子吸附、聚合及钯离子洗脱等工艺步骤,所制备材料实现记忆性选择分离钯离子。In view of this, the purpose of the present invention is to provide a preparation method and product for selectively separating palladium ion adsorption materials. The present invention combines silica gel with graphene oxide, and further introduces the surface of the composite material into dual Bonds and mercapto groups, and then the material is subjected to palladium ion adsorption, polymerization and palladium ion elution and other process steps, and the prepared material realizes memory selective separation of palladium ions.
为实现上述发明目的,本发明具体提供了如下所述技术方案:In order to realize the above-mentioned purpose of the invention, the present invention specifically provides the following technical solutions:
1、一种选择性分离钯离子吸附材料的制备方法,包括如下步骤:1, a kind of preparation method of selective separation palladium ion adsorption material, comprises the steps:
1)将活化硅胶分散于甲苯中,搅拌条件下继续加入γ-氨丙基三乙氧基硅烷和苯胺,加热保持反应物100~120℃温度条件下,搅拌回流反应3~24h,待反应结束后抽滤得固体,得到含有氨基的硅胶复合材料,并标记为SiO2-NH2;1) Disperse the activated silica gel in toluene, continue to add γ-aminopropyltriethoxysilane and aniline under stirring conditions, heat and keep the reactant at 100-120°C, stir and reflux for 3-24 hours, and wait for the reaction to complete After suction filtration, the solid was obtained to obtain a silica gel composite material containing amino groups, which was labeled as SiO 2 -NH 2 ;
2)将氧化石墨烯分散于N,N-二甲基甲酰胺并超声30min得混合物A,进一步向混合物A中加入步骤1)所得SiO2-NH2和催化剂N,N-二环己基碳二亚胺,保持反应物加热至40-80℃温度条件下反应20-35h,进一步抽滤得固体,将固体于真空30-60℃温度条件下干燥8-12h,得负载了氧化石墨烯的硅胶复合材料,标记为SiO2@GO;2) Disperse graphene oxide in N,N-dimethylformamide and sonicate for 30 minutes to obtain mixture A, and further add SiO 2 -NH 2 obtained in step 1) and catalyst N,N-dicyclohexylcarbodiene to mixture A For imine, keep the reactant heated to 40-80°C for 20-35h, and further filter to obtain a solid, then dry the solid under vacuum at 30-60°C for 8-12h to obtain graphene oxide-loaded silica gel Composite material, labeled SiO 2 @GO;
3)将步骤2)中所得SiO2@GO分散于甲苯中得混合物B,在搅拌状态下,向混合物B中加入N-氨乙基-γ-氨丙基三乙氧基硅烷和γ-巯丙基三甲氧基硅烷,加热至80-120℃并回流15~17h,抽滤所得固体于110℃下干燥12h得同时含有氨基和巯基的硅胶/氧化石墨烯基复合材料,标记为SiO2@GO-NH2-SH;3) Disperse SiO 2 @GO obtained in step 2) in toluene to obtain mixture B, and add N-aminoethyl-γ-aminopropyltriethoxysilane and γ-mercapto to mixture B under stirring Propyltrimethoxysilane, heated to 80-120°C and refluxed for 15-17h, suction filtered the resulting solid and dried at 110°C for 12h to obtain a silica gel/graphene oxide-based composite material containing both amino groups and mercapto groups, marked as SiO 2 @ GO-NH 2 -SH;
4)将步骤3)所得SiO2@GO-NH2-SH分散于醋酸溶液得混合物C,进一步向混合物C中加入马来酸酐,在常温下搅拌反应8-24h,抽滤所得固体用洗涤液多次洗涤,并于60-90℃温度条件下干燥8-12h,得同时带有双键和巯基的硅胶石墨烯材料,并标记为SiO2@A;4) Disperse the SiO 2 @GO-NH 2 -SH obtained in step 3) in the acetic acid solution to obtain a mixture C, further add maleic anhydride to the mixture C, stir and react at room temperature for 8-24 hours, and filter the obtained solid with washing liquid Washing several times, and drying at 60-90°C for 8-12 hours, a silica-graphene material with double bonds and mercapto groups was obtained, which was marked as SiO 2 @A;
5)将步骤4)所得SiO2@A置于含钯溶液中得混合物D,将混合物D静置吸附饱和,进一步抽滤所得固体在80-110℃温度条件下干燥8-12h,得到吸附了钯离子的材料,标记为SiO2@A-Pd;5) Put the SiO 2 @A obtained in step 4) into a palladium-containing solution to obtain a mixture D, let the mixture D stand for adsorption and saturation, and further filter the obtained solid with suction and dry it for 8-12 hours at a temperature of 80-110°C to obtain the adsorbed Materials with palladium ions, marked as SiO 2 @A-Pd;
6)将步骤5)中所得到SiO2@A-Pd分散于乙腈溶剂中得混合物E,依次向混合物E中加入AIBN和EGDMA,然后将整个反应体系在N2氛围条件下进行,于60℃的条件下搅拌反应10-24h,抽滤所得固体用洗涤液多次洗涤,并于40-60℃的真空干燥箱中干燥8-12h;6) Disperse the SiO 2 @A-Pd obtained in step 5) in an acetonitrile solvent to obtain a mixture E, add AIBN and EGDMA to the mixture E in turn, and then carry out the whole reaction system under the N 2 atmosphere, at 60°C The reaction was stirred for 10-24 hours under the conditions of the suction filtration, and the solid obtained by suction filtration was washed with washing liquid for several times, and dried in a vacuum oven at 40-60 °C for 8-12 hours;
7)用洗脱液将步骤6)中所得到产品中吸附的钯离子全部洗脱,即得到对钯离子有选择性吸附作用的印记聚合物材料,所述洗脱液由HCl、硫酸、硝酸中的一种或几种和硫脲组成,其中HCl、硫酸、硝酸浓度为0.05~2mol/L,硫脲质量分数为25-50%。7) All the palladium ions adsorbed in the product obtained in step 6) are eluted with an eluent to obtain an imprinted polymer material that selectively adsorbs palladium ions, and the eluent is composed of HCl, sulfuric acid, nitric acid One or more of them are composed of thiourea, wherein the concentrations of HCl, sulfuric acid and nitric acid are 0.05-2 mol/L, and the mass fraction of thiourea is 25-50%.
优选的,步骤1)中所述活化硅胶的制备方法为:将层析硅胶分散于1-10mol/L的盐酸、硫酸、硝酸或磺酸中的一种或几种,加热至60-120℃,搅拌反应3-24h后抽滤,用去离子水将其洗涤至中性,于110℃干燥箱中干燥12h,得到活化硅胶。Preferably, the preparation method of the activated silica gel described in step 1) is: disperse the chromatography silica gel in one or more of 1-10 mol/L hydrochloric acid, sulfuric acid, nitric acid or sulfonic acid, and heat it to 60-120°C , stirred and reacted for 3-24 hours, then filtered with suction, washed with deionized water until neutral, and dried in a drying oven at 110°C for 12 hours to obtain activated silica gel.
优选的,步骤1)所述活化硅胶与甲苯的质量体积比(g/mL)为4%~40%,所述活化硅胶与γ-氨丙基三乙氧基硅烷的质量体积比(g/mL)为1:0.3~2,活化硅胶与苯胺之间的质量体积比(g/mL)为100:0.1~5。Preferably, the mass volume ratio (g/mL) of the activated silica gel to toluene in step 1) is 4% to 40%, and the mass volume ratio (g/mL) of the activated silica gel to γ-aminopropyltriethoxysilane mL) is 1:0.3~2, and the mass volume ratio (g/mL) between activated silica gel and aniline is 100:0.1~5.
优选的,步骤2)所述混合物A中氧化石墨烯与N,N-二甲基甲酰胺的质量体积比(g/mL)为0.1%~1%,所述氧化石墨烯与SiO2-NH2的质量比为0.01~0.5:1。Preferably, the mass volume ratio (g/mL) of graphene oxide and N,N-dimethylformamide in the mixture A in step 2) is 0.1% to 1%, and the graphene oxide and SiO 2 -NH The mass ratio of 2 is 0.01-0.5:1.
优选的,步骤3)所述混合物B中SiO2@GO与甲苯质量体积比(g/ml)为2%~40%,所述SiO2@GO与N-氨乙基-γ-氨丙基三乙氧基硅烷质量体积比(g/mL)为1:0.1~1,所述SiO2@GO与γ-巯丙基三甲氧基硅烷质量体积比(g/mL)为1:0.2~2。Preferably, the mass volume ratio (g/ml) of SiO 2 @GO and toluene in the mixture B in step 3) is 2% to 40%, and the SiO 2 @GO and N-aminoethyl-γ-aminopropyl The mass volume ratio (g/mL) of triethoxysilane is 1:0.1~1, and the mass volume ratio (g/mL) of SiO 2 @GO and γ-mercaptopropyltrimethoxysilane is 1:0.2~2 .
优选的,步骤4)所述混合物C中SiO2@GO-NH2-SH质量分数为3%-8%,所述马来酸酐与SiO2@GO-NH2-SH的质量比为4~6:1。Preferably, the mass fraction of SiO 2 @GO-NH 2 -SH in the mixture C in step 4) is 3%-8%, and the mass ratio of maleic anhydride to SiO 2 @GO-NH 2 -SH is 4~ 6:1.
优选的,步骤5)所述含钯溶液浓度为100-2000mg/L,所述混合物D中SiO2@A质量分数为2%-8%。Preferably, the concentration of the palladium-containing solution in step 5) is 100-2000 mg/L, and the mass fraction of SiO 2 @A in the mixture D is 2%-8%.
优选的,步骤6)所述混合物E中SiO2@A-Pd质量分数为4%-25%,SiO2@A-Pd与AIBN的质量比为20-60:1,SiO2@A-Pd与EGDMA的质量体积比(g/mL)为1~2:2~1。Preferably, the mass fraction of SiO 2 @A-Pd in the mixture E in step 6) is 4%-25%, the mass ratio of SiO 2 @A-Pd to AIBN is 20-60:1, and the SiO 2 @A-Pd The mass volume ratio (g/mL) to EGDMA is 1~2:2~1.
优选的,步骤4)和步骤6)所述洗涤液为无水乙醇。Preferably, the washing solution in step 4) and step 6) is absolute ethanol.
2、根据上述任一项所述制备方法得到的选择性分离钯离子吸附材料。2. The selective separation palladium ion adsorption material obtained according to the preparation method described in any one of the above.
以上技术方案中,AIBN为偶氮二异丁腈,EGDMA为二甲基丙烯酸乙二醇酯。In the above technical scheme, AIBN is azobisisobutyronitrile, and EGDMA is ethylene glycol dimethacrylate.
本发明有益效果在于:The beneficial effects of the present invention are:
1)本发明首先使用酸对硅胶进行活化,再使用γ-氨丙基三乙氧基硅烷、苯胺和活化后的硅胶反应,实现硅胶表面带有氨基即SiO2-NH2,然后在SiO2-NH2表面接枝上氧化石墨烯。因为氧化石墨烯具有较大的比表面积(理论上可达2620m2/g),表面存在大量的羟基,可引入更多的功能基团,吸附材料表面的功能基团越多,吸附容量往往越大。但是,氧化石墨烯本身不能作为吸附材料,其原因在于:1、氧化石墨烯在水溶液中难以分离,即使使用高速离心机也难以实现分离,因此如果直接将氧化石墨烯加入水溶液中,它自身就是一种污染物,将造成水体环境污染;2、氧化石墨烯表面存在的功能基团为羟基、羧基和环氧基,这些含氧基团能够与绝大多数金属离子发生结合,对特定金属离子选择性差,因此对于某种特定金属离子的分离,尤其是贵金属(钯)离子的分离,需要结合其本身的特点,引入特定的功能基团,所以本发明采用进一步表面巯基及双键化,然后将材料进行吸附钯及洗脱钯等工艺步骤,即实现所制备材料具备记忆性选择分离钯离子的效果。1) In the present invention, an acid is used to activate the silica gel, and then γ-aminopropyltriethoxysilane and aniline are used to react with the activated silica gel, so that the surface of the silica gel has amino groups, that is, SiO 2 -NH 2 , and then the SiO 2 - Grafting graphene oxide on the surface of NH 2 . Because graphene oxide has a large specific surface area (theoretically up to 2620m 2 /g), there are a large number of hydroxyl groups on the surface, and more functional groups can be introduced. The more functional groups on the surface of the adsorption material, the higher the adsorption capacity. big. However, graphene oxide itself cannot be used as an adsorption material for the following reasons: 1. Graphene oxide is difficult to separate in aqueous solution, even with a high-speed centrifuge, so if graphene oxide is directly added to an aqueous solution, it itself is A pollutant that will cause water environmental pollution; 2. The functional groups on the surface of graphene oxide are hydroxyl, carboxyl and epoxy groups. The selectivity is poor, so for the separation of certain specific metal ions, especially the separation of precious metal (palladium) ions, it is necessary to combine its own characteristics and introduce specific functional groups, so the present invention adopts further surface sulfhydryl groups and double bonds, and then The material is subjected to process steps such as adsorption of palladium and elution of palladium, that is, the effect of the prepared material having memory selective separation of palladium ions is realized.
2)本发明公开的材料对钯离子的吸附率高,对溶液中钯离子选择性好,并且该材料可实现多次重复使用,且吸附性能基本不变。2) The material disclosed in the present invention has a high adsorption rate for palladium ions and good selectivity for palladium ions in the solution, and the material can be reused many times without substantially changing the adsorption performance.
具体实施方式Detailed ways
下面将结合具体实施例对本发明做进一步描述;The present invention will be further described below in conjunction with specific embodiment;
实施例1Example 1
一种选择性分离钯离子吸附材料的制备方法,包括如下步骤:A preparation method for selectively separating palladium ion adsorption materials, comprising the steps of:
1)向1000mL三口烧瓶中加入60g层析硅胶和500mL,6mol/L盐酸溶液,加热至110℃,搅拌回流8h,反应完成后用大量去离子水将其洗涤至中性,置于110℃下干燥12h得到活化硅胶。1) Add 60g of chromatographic silica gel and 500mL of 6mol/L hydrochloric acid solution into a 1000mL three-neck flask, heat to 110°C, stir and reflux for 8h, wash it with a large amount of deionized water until neutral after the reaction is completed, and place it at 110°C Dry for 12h to obtain activated silica gel.
2)将25g活化硅胶分散于400mL甲苯溶液中,在搅拌的条件下加入25mLγ-氨丙基三乙氧基硅烷,最后加入5mL苯胺,在加热至110℃温度条件下搅拌回流反应24h,经抽滤后,将固体于110℃干燥箱中干燥12h得到氨基硅胶;2) Disperse 25g of activated silica gel in 400mL of toluene solution, add 25mL of γ-aminopropyltriethoxysilane under stirring conditions, and finally add 5mL of aniline, and stir and reflux for 24 hours under the condition of heating to 110°C. After filtration, the solid was dried in a drying oven at 110°C for 12 hours to obtain amino silica gel;
3)将0.85g氧化石墨烯分散于350mL,N,N二甲基甲酰胺溶液中,超声30min使氧化石墨烯完全分散于溶液中,然后加入25g氨基硅胶和2.0gDCC,于60℃油浴锅中加热搅拌3天,反应完成后用无水乙醇反复多次洗涤抽滤,于60℃真空干燥箱中干燥12h,得到SiO2@GO;3) Disperse 0.85g of graphene oxide in 350mL, N,N dimethylformamide solution, ultrasonically disperse graphene oxide for 30min, then add 25g of amino silica gel and 2.0g of DCC, and place in a 60°C oil bath Heating and stirring at medium temperature for 3 days, after the reaction was completed, repeated washing and suction filtration with absolute ethanol, and drying in a vacuum oven at 60°C for 12 hours to obtain SiO 2 @GO;
4)将5gSiO2@GO分散于350mL甲苯溶液中,向小烧杯中加入5mLN-氨乙基-γ-氨丙基三乙氧基硅烷和10mLγ-巯丙基三甲氧基硅烷配制为混合液,在搅拌的条件下缓慢加入混合液,加热至100℃并回流反应15h后抽滤,于50℃真空干燥箱中干燥12h,即制备得到SiO2@GO-NH2-SH复合材料;4) Disperse 5g of SiO 2 @GO in 350mL of toluene solution, add 5mL of N-aminoethyl-γ-aminopropyltriethoxysilane and 10mL of γ-mercaptopropyltrimethoxysilane into a small beaker to prepare a mixed solution, Slowly add the mixed solution under the condition of stirring, heat to 100°C and reflux for 15 hours, then filter with suction, dry in a vacuum oven at 50°C for 12 hours, and the SiO 2 @GO-NH 2 -SH composite material is prepared;
5)向圆底烧瓶中加入2.0g SiO2@GO-NH2-SH,然后加入10g马来酸酐,最后加入50mLHAC,在常温下搅拌反应24h,待反应结束后,用无水乙醇多次洗涤抽滤得固体,将固体置于90℃干燥箱中干燥12h,得到含有双键和巯基的硅胶石墨烯材料5) Add 2.0g SiO 2 @GO-NH 2 -SH to the round bottom flask, then add 10g maleic anhydride, and finally add 50mL HAC, stir and react at room temperature for 24h, after the reaction is completed, wash with absolute ethanol several times The solid was obtained by suction filtration, and the solid was dried in a 90°C drying oven for 12 hours to obtain a silica gel graphene material containing double bonds and mercapto groups
6)将此材料放入含有钯离子浓度为1000mg/L的溶液中,待其吸附钯离子至饱和,于110℃下干燥12h;6) Put this material into a solution containing palladium ions with a concentration of 1000 mg/L, wait for it to absorb palladium ions to saturation, and dry at 110°C for 12 hours;
7)然后向三口烧瓶中加入3g吸附了钯离子的吸附材料,加入120mL乙腈作为溶剂,依次加入150mgAIBN,1mLEGDMA,再向三口烧瓶中充入N2,使整个反应体系在无氧的条件下进行,最后置于60℃的油浴锅中搅拌反应24h,待反应结束后,用无水乙醇多次洗涤,于60℃的真空干燥箱中干燥24h,干燥完成后,配制0.16mol/LHCl+50wt%硫脲的洗脱液,将材料中吸附的钯离子全部洗脱,便形成了钯离子空腔,即得到对钯离子有选择性吸附的钯离子印迹聚合物。7) Then add 3g of the adsorption material that has adsorbed palladium ions into the three-necked flask, add 120mL acetonitrile as a solvent, add 150mgAIBN, 1mLEGDMA in turn, and then fill the three-necked flask with N2 , so that the entire reaction system is carried out under anaerobic conditions. , and finally placed in an oil bath at 60°C and stirred for 24 hours. After the reaction, wash with absolute ethanol several times, and dry in a vacuum oven at 60°C for 24 hours. After drying, prepare 0.16mol/LHCl+50wt % thiourea eluent, all the palladium ions adsorbed in the material are eluted, and a palladium ion cavity is formed, that is, a palladium ion-imprinted polymer selectively adsorbing palladium ions is obtained.
实施例2Example 2
一种选择性分离钯离子吸附材料的制备方法,包括如下步骤:A preparation method for selectively separating palladium ion adsorption materials, comprising the steps of:
1)所述活化硅胶的制备与实施例1步骤1)所述相同。1) The preparation of the activated silica gel is the same as described in step 1) of Example 1.
2)所述氨基硅胶的制备与实施例1步骤2)所述相同。2) The preparation of the amino silica gel is the same as described in step 2) of Example 1.
3)将0.85g氧化石墨烯分散于350mLN,N二甲基甲酰胺溶液中,超声30min使氧化石墨烯完全分散于溶液中,然后加入85g氨基硅胶和2.0gDCC,于60℃油浴锅中加热搅拌3天,反应完成后用无水乙醇反复多次洗涤抽滤,于60℃真空干燥箱中干燥12h,得到SiO2@GO;3) Disperse 0.85g of graphene oxide in 350mL N,N dimethylformamide solution, ultrasonically disperse graphene oxide for 30min, then add 85g of amino silica gel and 2.0g of DCC, heat in an oil bath at 60°C Stir for 3 days. After the reaction is completed, wash and filter repeatedly with absolute ethanol, and dry in a vacuum oven at 60°C for 12 hours to obtain SiO 2 @GO;
4)将5gSiO2@GO分散于250mL甲苯溶液中,向小烧杯中加入2.5mLN-氨乙基-γ-氨丙基三乙氧基硅烷和5mLγ-巯丙基三甲氧基硅烷配制为混合液,在搅拌的条件下缓慢加入混合液,加热至120℃并回流反应15h后抽滤,于50℃真空干燥箱中干燥12h,即制备得到SiO2@GO-NH2-SH复合材料;4) Disperse 5g of SiO 2 @GO in 250mL of toluene solution, add 2.5mL of N-aminoethyl-γ-aminopropyltriethoxysilane and 5mL of γ-mercaptopropyltrimethoxysilane into a small beaker to prepare a mixed solution , slowly add the mixed solution under the condition of stirring, heat to 120°C and reflux for 15 hours, then filter with suction, and dry in a vacuum oven at 50°C for 12 hours, and the SiO 2 @GO-NH 2 -SH composite material is prepared;
5)向圆底烧瓶中加入2.0g SiO2@GO-NH2-SH,然后加入2g马来酸酐,最后加入50mLHAC,在常温下搅拌反应24h,待反应结束后,用无水乙醇多次洗涤抽滤得固体,将固体置于90℃干燥箱中干燥12h,得到含有双键和巯基的硅胶/氧化石墨烯基复合材料;5) Add 2.0g SiO 2 @GO-NH 2 -SH to the round bottom flask, then add 2g maleic anhydride, and finally add 50mL HAC, stir and react at room temperature for 24h, after the reaction is completed, wash with absolute ethanol several times The solid was obtained by suction filtration, and the solid was dried in a 90°C drying oven for 12 hours to obtain a silica gel/graphene oxide-based composite material containing double bonds and mercapto groups;
6)将此材料放入含有钯离子浓度为1000mg/L的溶液中,待其吸附钯离子至饱和,于110℃下干燥12h;6) Put this material into a solution containing palladium ions with a concentration of 1000 mg/L, wait for it to absorb palladium ions to saturation, and dry at 110°C for 12 hours;
7)然后向三口烧瓶中加入3g吸附了钯离子的吸附材料,加入120mL乙腈作为溶剂,依次加入50mgAIBN,3mL EGDMA,再向三口烧瓶中充入N2,使整个反应体系在无氧的条件下进行,最后置于60℃的油浴锅中搅拌反应24h,待反应结束后,用无水乙醇多次洗涤,于60℃的真空干燥箱中干燥24h,干燥完成后,配制0.16mol/LHCl+50wt%硫脲的洗脱液,将材料中吸附的钯离子全部洗脱,便形成了钯离子空腔,即得到对钯离子有选择性吸附的钯离子印迹聚合物。7) Then add 3g of the adsorption material that has adsorbed palladium ions into the three-necked flask, add 120mL of acetonitrile as a solvent, add 50mgAIBN, 3mL of EGDMA in turn, and then fill the three-necked flask with N 2 to make the entire reaction system under anaerobic conditions Finally, place it in an oil bath at 60°C and stir for 24 hours. After the reaction is over, wash it with absolute ethanol several times, and dry it in a vacuum oven at 60°C for 24 hours. After drying, prepare 0.16mol/L HCl+ The eluent of 50wt% thiourea elutes all the palladium ions adsorbed in the material, forming a palladium ion cavity, that is, obtaining a palladium ion-imprinted polymer selectively adsorbing palladium ions.
选择性吸附钯离子性能测试:Selective adsorption palladium ion performance test:
以实施例1所得材料进行选择性实验:称取2.0g的钯离子印迹聚合物,装入固定床(直径6mm,高度100mm)中,将含钯废液以1mL/min的流速通过固定床,所述含钯废液中还包含多种其他金属离子(如图1下标所示),最后计算各种金属离子的吸附容量。吸附容量的计算公式:Selectivity experiment was carried out with the material obtained in Example 1: Weigh 2.0 g of palladium ion-imprinted polymer, put it into a fixed bed (diameter 6 mm, height 100 mm), pass the palladium-containing waste liquid through the fixed bed at a flow rate of 1 mL/min, The palladium-containing waste liquid also contains various other metal ions (as shown in the subscript of FIG. 1 ), and finally the adsorption capacity of various metal ions is calculated. The calculation formula of adsorption capacity:
其中公式中:m表示钯离子印迹聚合物的质量(g),c0表示各种金属离子的初始浓度(mg/L),cf表示固定床流出液中各种金属离子的浓度(mg/L),V表示流出液的体积(L)。Wherein in the formula: m represents the quality (g) of palladium ion imprinted polymer, c 0 represents the initial concentration (mg/L) of various metal ions, c f represents the concentration (mg/L) of various metal ions in the fixed bed effluent L), V represents the volume (L) of the effluent.
吸附后对各类金属离子进行测量计算,得到如图1所示的吸附容量图,由图1实验结果表明吸附材料对钯离子具有显著的识别特性和亲和能力。进一步对实施例2所制备材料进行选择性吸附钯离子性能测试,同样显示其具有对钯离子具有显著的识别特性和亲和能力。After adsorption, various metal ions were measured and calculated, and the adsorption capacity diagram shown in Figure 1 was obtained. The experimental results in Figure 1 show that the adsorption material has significant recognition characteristics and affinity for palladium ions. The material prepared in Example 2 was further tested for the selective adsorption of palladium ions, which also showed that it had significant recognition characteristics and affinity for palladium ions.
将吸附后的复合材料再经10mL,6mol/L盐酸和30g/L的硫脲组成的混合溶液洗脱,复合材料的最大动态饱和吸附容量和富集因子均未出现明显降低,可实现废水溶液中钯离子的全部分离、回收。由以上实施例进一步论证了本发明公开的复合材料对钯离子的吸附率高,对溶液中钯离子选择性好,并且该材料可实现多次重复使用,且吸附性能基本不变。After the adsorbed composite material was eluted with a mixed solution composed of 10mL, 6mol/L hydrochloric acid and 30g/L thiourea, the maximum dynamic saturated adsorption capacity and enrichment factor of the composite material did not decrease significantly, and the waste water solution could be realized All the separation and recovery of palladium ions in the medium. The above examples further demonstrate that the composite material disclosed in the present invention has a high adsorption rate for palladium ions, good selectivity for palladium ions in solution, and the material can be reused many times, and the adsorption performance is basically unchanged.
最后说明的是,以上对本发明的具体实施方式作了详细说明,但是本发明并不限于上述实施方式,在本领域普通技术人员所具备的知识范围内,还可以在不脱离本发明宗旨的前提下作出各种变化。Finally, it is noted that the specific embodiments of the present invention have been described in detail above, but the present invention is not limited to the above-mentioned embodiments. Make various changes below.
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