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首页> 外文期刊>Journal of Colloid and Interface Science >Surface binding site analysis of Ca~(2+)-homoionized clay-humic acid complexes
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Surface binding site analysis of Ca~(2+)-homoionized clay-humic acid complexes

机译:Ca〜(2 +)-均质化粘土-腐植酸复合物的表面结合位点分析

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Clay-humic substance complexes play a major role in controlling the mobility of toxic metals in contaminated soils. However, our understanding of the underlying mechanisms is limited. Binding site analysis of clay and clay-mineral-humic composites, in this study, revealed an enhanced surface reactivity for the clay surface by the sorbed humic substances. Kaolinite and illite had three binding sites with pK_a values ranging from ~4.5 to 9.6 at Ca~(2+) concentrations of 0.01 and 0.1M respectively. In the presence of peat humic acid (PHA), four or five binding sites were observed for humics sorbed kaolinite surface at Ca~(2+) concentrations of 0.01 and 0.1M respectively. pK_a values ranged from ~4.4 to 9.6 for humic acid concentration of 0.01 and 0.1mg/mL. For illite, four or five binding sites were found with pK_as ranging from ~4.1 to 9.4. From zeta potential measurements of PHA-kaolinite or PHA-illite suspensions, the already negative potential decreased by 30mV from pH 4 to 7, and by 10mV for pH values greater than 7. For illite the initial negative surface potential decreased by 15mV up to a pH of 9. Above this pH, the potential decrease diminished to 2 or 5mV. These changes in surface potential confirm the adsorption of PHA to the clay mineral surface. FTIR measurements of clay samples were able to identify the kaolinite and illite phases. In addition, FTIR absorption bands found in the range of 1950-1800cm~(-1), suggest the interaction of PHA with kaolinite and illite surfaces. The results of this study indicate that the sorption of humic substances increases the availability of clay surface functional groups for deprotonation and potential sorption of toxic metal cations.
机译:粘土腐殖质复合物在控制有毒金属在受污染土壤中的迁移中起着重要作用。但是,我们对基本机制的理解是有限的。在这项研究中,对粘土和粘土-矿物-腐殖质复合材料的结合位点分析表明,吸附的腐殖质可增强粘土表面的表面反应性。高岭石和伊利石具有三个结合位点,在Ca〜(2+)浓度分别为0.01和0.1M时,pK_a值在〜4.5至9.6之间。在泥炭腐殖酸(PHA)存在下,在Ca〜(2+)浓度分别为0.01和0.1M时,腐殖质吸附的高岭石表面观察到四个或五个结合位点。当腐殖酸浓度为0.01和0.1mg / mL时,pK_a值在〜4.4至9.6之间。对于伊利石,发现有四个或五个结合位点,pK_as的范围为〜4.1至9.4。根据对PHA-高岭石或PHA-伊利石悬浮液的zeta电位测量,从pH 4到7,已经为负的电位降低了30mV;对于pH大于7的溶液,已经为负的电位降低了10mV。 pH值为9。高于此pH值,电位下降减小到2或5mV。这些表面电势的变化证实了PHA在粘土矿物表面的吸附。粘土样品的FTIR测量能够识别高岭石和伊利石相。此外,在1950-1800cm〜(-1)范围内发现FTIR吸收带,表明PHA与高岭石和伊利石表面发生相互作用。这项研究的结果表明,腐殖质的吸附增加了用于去质子化和潜在吸附有毒金属阳离子的粘土表面官能团的利用率。

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