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Speciation and Mobility Assessment of Heavy Metals in the Coastal Municipal Solid Waste Incinerator Ash Landfill

机译:沿海城市生活垃圾焚烧炉灰垃圾填埋场中重金属的形态和迁移率评估

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In the metropolitan areas of Japan, coastal landfills have become a practical and main solution for the disposal of municipal solid waste incinerator ash (MSWIA) due to limited inland space. Leachate from the landfilled MSWIA contains many dissolved and suspended substances harmful to the surrounding environment, particularly heavy metals, such as lead, zinc, and cadmium. The mobility assessment of these heavy metals is therefore one of the important environmental issues for the coastal landfill. In this paper, modified batch tests were conducted to investigate the effects of pH and E_h changes on the mobility of heavy metals in both MSWIA and marine clay layer. Based on the speciation of heavy metals by using a sequential extraction method in the leachate-MSWIA and leachate-marine clay systems, heavy metal mobility and availability were discussed with the comparison to large-scale model test results presented by (Kamon et al. "Biochemical Effects on the Long-Term Mobility of Heavy Metals in Marine Clay at Coastal Landfill Sites," J. ASTM Int., Vol. 3, 2006), which provides the long-term change in heavy metal concentrations and forms in the coastal MSWIA landfill site. Under the high pH (-11) and low E_h (≈-200 mV) condition in the MSWIA-leachate system, Zn, Pb, and Cd were effectively immobilized by the formation of the reducible and oxidizable fractions of Zn and the oxidizable and residual (insoluble) fractions of Pb significantly. However, the potential mobility of Cd was relatively high since the formation of exchangeable compounds was more dominantly contributed to the immobilization. Test results on the speciation of the metals in the marine clay-leachate system accounts well for the evidence that the marine clay acts as the attenuation layer for heavy metals in leachate. These findings strongly support that heavy metal mobility is restricted in the coastal MSWIA landfill due to the formation of stable and insoluble forms under reduced-alkaline condition and the attenuation effect of the marine clay.
机译:在日本大都市地区,由于内陆空间有限,沿海垃圾填埋场已成为处理城市固体废物焚烧炉灰(MSWIA)的实用且主要解决方案。垃圾填埋场产生的渗滤液含有许多对周围环境有害的溶解和悬浮物质,尤其是重金属,例如铅,锌和镉。因此,这些重金属的迁移率评估是沿海垃圾填埋场的重要环境问题之一。在本文中,进行了改进的分批测试,以研究pH和E_h变化对MSWIA和海洋粘土层中重金属迁移率的影响。根据在渗滤液-MSWIA和渗滤液-海洋黏土体系中采用顺序萃取方法对重金属进行的形态分析,讨论了重金属的迁移率和有效性,并与(Kamon等人提出的大规模模型测试结果进行了比较。生化效应对沿海填埋场海洋黏土中重金属的长期迁移的影响,” J。ASTM Int。,第3卷,2006年),该报告提供了沿海MSWIA中重金属浓度和形式的长期变化垃圾填埋场。在MSWIA渗滤液系统中的高pH(-11)和低E_h(≈-200mV)条件下,Zn,Pb和Cd通过形成Zn的可还原和可氧化级分以及可氧化和残留而有效地固定化(不溶)的Pb分数明显。但是,Cd的潜在迁移率较高,因为可交换化合物的形成对固定化的贡献更大。关于海洋粘土-沥滤液系统中金属形态的测试结果很好地说明了海洋粘土充当渗滤液中重金属的衰减层的证据。这些发现有力地证明了重金属迁移率在沿海MSWIA垃圾填埋场受到限制,这是由于在碱性还原条件下形成了稳定和不溶的形式以及海洋粘土的衰减作用。

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