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Cysteine-metal affinity chromatography: determination of heavy metal adsorption properties

机译:半胱氨酸-金属亲和色谱:重金属吸附性能的测定

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Various adsorbent materials have been reported in the literature for heavy metal removal. We have developed a novel approach to obtain high metal sorption capacity utilising cysteine containing adsorbent. Metal complexing aminoacid-ligand cysteine was immobilised inot poly(hydroxyethylmethacrylate) (PHEMA) microbeads. PHEMA-cysteine affinity microbeads containing 0.138 mmol cysteine/g were used in the removal of heavy metal ions (i.e. copper, lead and cadmium) from aqueous media containing different amounts of these ions (50-400 mg/l for Pb(II) and Cd(II), 25-60 mg/l for Cu(II) and at different pH values (4.0-7.0). The maximum adsorption capacity of heavy metal ions onto the cysteine-containing microbeads under non-competitive conditions were 0.259 mmolg for Pb(II), 0.330 mmol/g for Cd(II) and 0.229 mmol/g for Cu(II). The affinity order was obsrved as follows: Cd(II)>Pb(II)>Cu(II). The competitive adsorption capacities of the heavy metals were 0.0260 mmol/g for Cd(II) and 0.120 mmol/g for Cu(II). Pb(II) adsorption onto cysteine-immobilised microbeads was zero under competitive conditions. the affinity order was as follows: Cd(II)>Cu(II)>Pb(II). The formation constants of cysteine-metal ion complexes have been investigated applying the method of Ruzic. The calculated value of stability constants were 1.75X10~4 l/mol for Pb(II)-cysteine complex and 4.35X10~4 l/mol for Cd(II)-cysteine compelx and 1.39X104 lmol for Cu(II)-cysteine complex. PHEMA microbeads carrying cysteine can be regenerated by washing with a solution of hydrochloric acid (0.05 M). The maximum desorption ratio was greater than 99%. These PHEMA microbeads are suitable for repeated use for more than three adsorption-desorption cycles without considerable loss in adsorption capacity.
机译:在文献中已经报道了各种吸附剂材料以去除重金属。我们已经开发出一种新颖的方法来利用含半胱氨酸的吸附剂获得高的金属吸附能力。金属络合氨基酸-配体半胱氨酸被固定在聚甲基丙烯酸羟乙酯(PHEMA)微珠上。含有0.138 mmol半胱氨酸/ g的PHEMA-半胱氨酸亲和微珠用于从含有不同量这些离子(对于Pb(II)为50-400 mg / l)的水性介质中去除重金属离子(即铜,铅和镉)。 Cd(II),Cu(II)在不同pH值(4.0-7.0)下为25-60 mg / l。在非竞争条件下,重金属离子在含半胱氨酸的微珠上的最大吸附能力为0.259 mmolg Pb(II),Cd(II)为0.330 mmol / g,Cu(II)为0.229 mmol / g,亲和力顺序为:Cd(II)> Pb(II)> Cu(II)。 Cd(II)对重金属的吸附容量为0.0260 mmol / g,Cu(II)对重金属的吸附容量为0.120 mmol / g。在竞争条件下,半胱氨酸固定的微珠对Pb(II)的吸附为零,亲和力顺序为: Cd(II)> Cu(II)> Pb(II)。使用Ruzic方法研究了半胱氨酸-金属离子配合物的形成常数,计算的稳定常数为对于Pb(II)-半胱氨酸复合物为1.75X10〜4 l / mol,对于Cd(II)-半胱氨酸复合物为4.35X10〜4 l / mol,对于Cu(II)-半胱氨酸复合物为1.39X104 lmol。携带半胱氨酸的PHEMA微珠可通过用盐酸溶液(0.05 M)洗涤而再生。最大脱附率大于99%。这些PHEMA微珠适合重复使用三个以上的吸附-解吸循环,而不会显着降低吸附容量。

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