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ADSORPTION BEHAVIOR OF FULVIC ACID, COPPER, AND THEIR COMPLEX ONTO CLAY MINERALS

机译:富含酸,铜及其复合物在粘土矿物质上的吸附行为

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In Japanese landfill sites, municipal solid waste incineration residues (MSWIR) were mainly disposed. Although incineration reduce can reduce the volume of waste materials, many pollutants, especially heavy metals, were accumulated in MSWIR. That's why the leachates from landfdl sites were monitored and treated to evaluate the stabilization of the landfill sites even after the disposal was finished. However, it is difficult to evaluate the stabilization of heavy metals because the behaviors of heavy metals were complex such as adsorption to the organic compounds. Therefore, the long term behaviors of heavy metals in landfill site could not be explained with the scientific basis. For this reason, it is quite difficult to estimate necessary period for complete closure of a landfill site. On the other hand, as immobilization mechanisms of heavy metals in landfdl sites, it is well known like precipitations (CO3~(2-), S~(2-), SO4~(2-)) , adsorption to some materials (iron hydroxide, aluminum hydroxide, clay minerals). Furthermore, in the field of water environment, it is reported that humic substance was greatly related to the mobilization and accumulation of heavy metals especially copper, lead, zinc. This function of humic substances was expected as well as landfill site. In particular, it is well known that the mobilization of copper depends strongly on the complexation with dissolved organic matter (DOM) in natural environment. According to Van Zomeren et al, 82 to 100 % of copper in the leachate of landfilled MSWI bottom ash was bound by DOM including humic substances between pH 6.6 and 10.6. Therefore, in this study, copper was focused on because copper mobility in a landfdl body might strong relation with humic substance. In previous study, it was proved that the non-ideal competitive adsorption-Donnan (NICA-Donnan) model could describe the interaction between copper and fulvic acid in liquid phase. However, it was not researched so much about the behavior of copper after complexation with fulvic acid. So, the objective of this study was to investigate the adsorption behavior of copper, fulvic acid, and their complex onto clay minerals.
机译:在日本垃圾填埋场,主要征服市政固体废物焚烧残留物(MSWIR)。虽然焚烧减少可以减少废料的体积,但许多污染物,尤其是重金属累积在MSWIR中。这就是为什么监测和治疗Landfdl站点的渗滤液,以评估垃圾填埋场所的稳定性,即使在处置完成后也是如此。然而,难以评估重金属的稳定性,因为重金属的行为是复合的,例如对有机化合物的吸附。因此,无法以科学依据解释垃圾填埋场中重金属的长期行为。因此,估计垃圾填埋场的完全关闭是非常困难的。另一方面,作为Landfdl位点中重金属的固定机制,众所周知的沉淀(CO 3〜(2-),S〜(2-),SO4〜(2-)),对一些材料的吸附(铁氢氧化物,氢氧化铝,粘土矿物质)。此外,在水环境领域,据报道,腐殖质与重金属的动员和积累尤其是铜,铅,锌。预计腐殖物质和垃圾填埋场的这种功能。特别地,众所周知,铜的动员强烈取决于自然环境中与溶解有机物(DOM)的络合。根据van Zomeren等,82至100%的填埋Mswi底灰的浸出液中的铜制在pH 6.6和10.6之间的腐殖质物质包括DOM。因此,在这项研究中,铜的重点是因为Landfdl体中的铜迁移率可能与腐殖质的关系很强。在以前的研究中,证明了非理想的竞争吸附 - 寡南(NICA-DONNAN)模型可以描述液相中铜和富乙酸之间的相互作用。然而,在富含富甲酸络合后,它没有研究铜的行为。因此,本研究的目的是探讨铜,富乙酸及其复合物在粘土矿物上的吸附行为。

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