共查询到19条相似文献,搜索用时 109 毫秒
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果葡糖分离络合载体性能研究 总被引:1,自引:0,他引:1
55%高果糖浆和90%高果糖浆以其高甜度、低热量和高果糖含量等功能而广泛应用于生产和生活中.如何以低廉的价格、合理的生产条件分离42%果葡糖浆是研究人员一直在探索的一个首要问题.李惟等[1,2]曾将带有硼羟基的功能手臂-氨基苯硼酸通过偶氮反应共价连接到多孔聚苯乙烯载体上,制备出硼酸基络合载体,并在长径比175:1条件下,将42%果葡糖进行有效分离,所得果糖纯度为99%,回收率为99%.上述结果表明,这种新型果糖载体极有可能在果葡糖分离工业中得以应用.本文在此基础上,对大孔硼酸基聚苯乙烯树脂的吸附… 相似文献
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大孔树脂分离纯化楮果总黄酮优化工艺研究 总被引:1,自引:0,他引:1
筛选适合分离纯化楮果总黄酮的大孔树脂并确定最优工艺条件。以静态吸附率和解吸率为指标对8种大孔树脂进行筛选,确定D101树脂的分离纯化效果最佳。通过动态吸附实验考察上样流速、上样溶液pH值、上样溶液浓度、乙醇浓度、洗脱流速、洗脱剂用量等工艺条件对分离纯化效果的影响,确定最优工艺条件如下:上样流速为2BV/h,pH值为6,上样溶液浓度为0.05mg/mL,80%乙醇作洗脱剂,洗脱流速为5BV/h,洗脱剂用量为7.5BV。采用最优工艺条件,楮果总黄酮含量提高至22.26%,产品精制倍数为4.79,表明D101树脂能有效纯化楮果总黄酮。 相似文献
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大孔树脂分离提取麻黄碱的研究 总被引:20,自引:1,他引:20
本文研究了九种大孔吸附树脂对麻黄碱的吸附能力,其中以D151,XAD-4,XAD-7的吸附效果较好,静态吸附容量分别为240.4mg/ml,122.1mg/ml,87.2mg/ml。三种树脂最佳吸附pH值为11,D151和XAD-7采用.08mol/L的HCl洗脱,XAD-4采用0.02mol/L的HCl与甲醇1:1的混合液洗脱。将三种树脂直接用于麻黄草提取液的麻黄碱分离提取,回收均在90%以上,纯度在80%以上,一次吸附提纯倍数为15-19倍。 相似文献
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国产大孔吸附树脂浓集分离赤霉素 总被引:1,自引:0,他引:1
研究了7种国产大孔吸附树脂对赤霉素的吸附能力,其中S-8吸附效果较好,赤霉素固/液分配系数为12.44,动态吸附容量为4.06mg/ml。80%丙酮水地赤霉素的洗脱能力较强。用工业赤霉素发酵液进行吸附-解吸实验,分配系数可提高至25.88(PH=2),动态吸附容量可提高至10.02mg/ml,赤霉素收率可达90%以上,且经吸附-解吸循环,可将发酵液中赤霉素浓缩7倍以上。 相似文献
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大孔离子交换树脂分离纯化玻璃酸的研究 总被引:6,自引:0,他引:6
本文选用了四种离子交换树脂进行分离纯化玻璃酸的研究。结果采用D315大孔离子交换树脂,以去离子水为淋洗液,0.6mol/L NaCl溶液为洗脱液,纯化效果较佳,纯化产品杂蛋白含量≤0.3%,回收率达71.1%,粘均分子量大于96万。 相似文献
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IntroductionThe preconcentration and separation of elements in samples by means of a chelateresin[l--5J or a chelate fibre[6'7J have been reported. However, the synthesis of the resin or thefibre usually takes a long time and a complex synthetic process. Accordingly, the epoxy--tan-ning chelate resin[8] and the epoxy-urea chelate .esin[9] have been synthesized and used for thepreconcentration of trace elements. However, these chelate resins could not be used for theenrichment of trace element… 相似文献
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研究Diaion HP–20大孔吸附树脂分离纯化含羞草种子中黄酮类物质的工艺条件。用海南含羞草种子为原料,以含羞草种子中总黄酮吸附量和解吸率为评价指标,考察上样流量、洗脱液种类、柱径比、洗脱液流量等影响因素。Diaion HP–20大孔吸附树脂分离纯化含羞草种子中黄酮类物质的最佳工艺条件:上样流量3 m L/min,洗脱液为40%乙醇溶液,柱径比为1∶10,洗脱液流量为4 m L/min。该方法简单,可行,能够有效分离纯化含羞草种子中黄酮类物质,且大孔吸附树脂可重生,利用率高。 相似文献
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铑-铱分离-向被认为是最困难的课题之一,即使文献曾报道Rh-Ir的分离,但实际Rh并未与萃取剂或吸附剂反应,而是与非贵金属离子一同留在溶液中。我们曾用光谱半定量方法研究了AP树脂对Rh、Ir的吸附行为,结果是Rh不被吸附而Ir能被吸附。本文通过改变Rh的离子状态,使之能被AP树脂吸附完全,而与留在溶液中的非贵金属分离,然后在柱上用不同淋洗液再使Rh-Ir分离。 相似文献
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聚苯乙烯微球表面的聚集态结构和苯基堆砌 总被引:4,自引:0,他引:4
用扫描隧道显微镜(STM)研究微乳液聚合法制备的聚苯乙烯微球.STM图像显示这种聚苯乙烯微球的表面具有不同的聚集态结构.在表面的某些区域,聚合物链没有相互缠结现象,而是有序地堆积在一起.在适当的情况下,同一条链上的苯基还会堆砌起来,形成一种平行移位的结构,其类似于苯双分子的最稳定结构.还用STM研究了用苯溶胀过的聚苯乙烯粒子,并观察到了类似螺旋结构的聚合物链以及扭曲的聚合物链.在聚苯乙烯微球中,聚合物链段和苯基的有序堆砌状态的存在,是因为苯乙烯单体已经在微乳液内的某些区域堆砌成有序的状态. 相似文献
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Macroporous poly(vinyl acetate-co-triallyl isocyanurate)beads were prepared with suspension polymerization method.The copolymer beads were then transformed into poly(vinyl alcohol-co-triallyl isocyanurate)by ester exchange reaction.Aminocarboxylic acids were immobilized on the copolymer beads by the esterification of hydroxyl groups with diethyl-lenetriaminepentaacetic bisanhydride,The weak acid exchange capacities,specific surface areas and mean pore diameters of the rsultant resin beads were measured. 相似文献
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《Journal of separation science》2003,26(5):381-386
The solid‐phase extraction (SPE) of copper(II) and aluminium(III) from fresh waters on an ion‐exchange complexing resin containing iminodiacetic groups (Chelex 100) has been examined. Quantitative recovery of the metal ions was related to the breakthrough profile that, for some samples, could not be evaluated directly. A method is suggested for evaluation, instead, of the sorption curves, on the basis of passing different volumes of sample through the column. This enables evaluation of important properties, for instance the central point of the breakthrough curve, Vf. The column used was a small one, containing 0.10 g dry Chelex 100. The metal ion was eluted with a small volume of acid solution, 10 mL of 0.5 mol L–1 HNO3; this resulted in good preconcentration factors. For copper(II) it was found that fresh waters of similar composition could have different Vf in the same column. This was ascribed to different reaction coefficients (αM(I)) of copper(II) in the considered samples, which affects Vf. By use of the proposed SPE procedure it is possible to evaluate the reaction coefficient of copper(II). The values of αM(I) for two different drinking waters at pH 7.7 were found to be 3.70×1012 and less than 4.40×1011. Similar results were obtained for aluminium(III). 相似文献