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Thermally induced transformations of Fe oxide-stabilized residues from waste incineration

机译:废物焚烧产生的Fe稳定氧化物的热诱导转变

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摘要

Air pollution control (APC) facilities at waste incinerator plants produce large quantities of solid residues rich in salts and heavy metals. Heavy metals are readily released to water from the residues and it has ,therefore, been found suitable to apply a rapid co-precipitation/adsorption process as a means to immobilize the toxic elements. In the 'Ferrox process', this immobilization is based on coprecipitation with an Fe(III) oxide formed by oxidation of Fe (II) by air in an aqueous slurry with the APC residue at alkaline pH. In this work we have undertaken a Mossbauer spectroscopy study of the Fe oxide phase formed by precipitation at room temperature and of the oxides present after heating to 600 and 900 deg C. The only Fe oxide observed in the Ferrox product at room temperature is a very poorly crystalline ferrihydrite. Analytical transmission electron microscopy showed that the main elements associated with the ferrihydrite are Si and Ca. following heating to 600 deg C the oxide is still characterized as an amorphous Fe oxide, and it is probable that Si associated with the ferrihydrite is decisive in preventing crystallization. After the 900 deg C treatment a transformation into defect maghemite is observed. Reducing gases produced from carbon in the samples probably induces this transformation. It eases, thus, the reduction of Fe (III) and the consequent formation of magnetite that eventually oxidizes to maghemite during cooling in air .
机译:垃圾焚烧厂的空气污染控制(APC)设施产生大量富含盐和重金属的固体残留物。重金属很容易从残留物中释放到水中,因此,发现重金属适合用于快速共沉淀/吸附过程,以固定有毒元素。在“ Ferrox工艺”中,这种固定化是基于与Fe(III)氧化物的共沉淀,该氧化物是通过空气中的APC残留物在碱性pH下被空气中的Fe(II)氧化而形成的。在这项工作中,我们进行了Mossbauer光谱研究,研究了室温下析出形成的Fe氧化物相以及加热至600和900℃后存在的氧化物。在Ferrox产品中,在室温下观察到的唯一Fe氧化物是结晶性较弱的水铁矿。透射电子显微镜分析表明,与亚铁水合物有关的主要元素是硅和钙。加热到600摄氏度后,该氧化物仍被表征为无定形的Fe氧化物,与亚铁酸盐结合的Si可能在防止结晶方面起决定性作用。在900℃处理后,观察到向缺陷磁赤铁矿的转变。减少样品中碳产生的气体可能会引起这种转变。因此,它减轻了Fe(III)的还原以及由此形成的磁铁矿,该磁铁矿在空气中冷却时最终氧化成磁赤铁矿。

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