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Chemical associations and mobilization of heavy metals in fly ash from municipal solid waste incineration

机译:城市固体废物焚烧飞灰中的化学缔合和重金属的迁移

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This study focusses on chemical and mineralogical characterization of fly ash and leached filter cake and on the determination of parameters influencing metal mobilization by leaching. Three different leaching processes of fly ash from municipal solid waste incineration (MSWI) plants in Switzerland comprise neu-tral, acidic and optimized acidic (+ oxidizing agent) fly ash leaching have been investigated. Fly ash is characterized by refractory particles (Al-foil, unburnt carbon, quartz, feldspar) and newly formed high-temperature phases (glass, gehlenite, wollastonite) surrounded by characteristic dust rims. Metals are carried along with the flue gas (Fe-oxides, brass) and are enriched in mineral aggregates (quartz, feldspar, wollastonite, glass) or vaporized and condensed as chlorides or sulphates. Parameters controlling the mobilization of neutral and acidic fly ash leaching are pH and redox conditions, liquid to solid ratio, extraction time and temperature. Almost no depletion for Zn, Pb, Cu and Cd is achieved by performing neutral leaching. Acidic fly ash leaching results in depletion factors of 40% for Zn, 53% for Cd, 8% for Pb and 6% for Cu. The extraction of Pb and Cu are mainly limited due to a cementation process and the for-mation of a PbCu~0-alloy-phase and to a minor degree due to secondary precipitation (PbCl_2). The addition of hydrogen peroxide during acidic fly ash leaching (optimized acidic leaching) prevents this reduction through oxidation of metallic components and thus significantly higher depletion factors for Pb (57%), Cu (30%) and Cd (92%) are achieved. The elevated metal depletion using acidic leaching in combination with hydrogen peroxide justifies the extra effort not only by reduced metal loads to the environment but also by reduced deposition costs.
机译:这项研究的重点是粉煤灰和浸出的滤饼的化学和矿物学表征,以及影响浸出金属动员的参数的确定。研究了瑞士中性垃圾焚烧厂(MSWI)的三种不同的粉煤灰浸出工艺,包括中性,酸性和优化的酸性(+氧化剂)粉煤灰浸出。粉煤灰的特征是难熔颗粒(铝箔,未燃烧的碳,石英,长石)和新形成的高温相(玻璃,钠钙石,硅灰石)被特有的粉尘边缘包围。金属与烟气(氧化铁,黄铜)一起携带,并富含矿物质(石英,长石,硅灰石,玻璃)或蒸发并冷凝为氯化物或硫酸盐。控制中性和酸性粉煤灰浸出动员的参数是pH和氧化还原条件,液固比,萃取时间和温度。通过进行中性浸提,几乎没有锌,铅,铜和镉的消耗。酸性粉煤灰的浸出导致锌的损耗因子为40%,镉的损耗率为53%,铅的损耗率为8%,铜的损耗率为6%。 Pb和Cu的萃取主要受到胶结过程和PbCu〜0合金相的形成的限制,并且由于二次沉淀(PbCl_2)而受到的限制较小。在酸性粉煤灰浸出(优化的酸性浸出)过程中添加过氧化氢可防止金属成分氧化而导致这种还原,因此可显着提高Pb(57%),Cu(30%)和Cd(92%)的损耗因子。使用酸性浸提结合过氧化氢提高金属消耗量,不仅可以通过减少对环境的金属负荷,还可以通过减少沉积成本来证明额外的努力。

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