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Bottom ash is the major by-product of municipal solid waste incineration(MSWI), and is often reused as an engineering material, such as road-base aggregate. However, some metals(especially aluminum) in bottom ash can react with water and generate gas that could cause expansion and failure of products containing the ash; these metals must be removed before the ash is utilized. The size distribution and the chemical speciation of metals in the bottom ash from two Chinese MSWI plants were examined in this study, and the recovery potential of metals from the ash was evaluated. The metal concentrations in these bottom ashes were lower than that generated in other developed countries. Specifically, the contents of Al,Fe, Cu and Zn were 18.9–29.2, 25.5–32.3, 0.7–1.0 and 1.6–2.5 g/kg, respectively. Moreover,44.9–57.0 wt.% of Al and 55.6–75.4 wt.% of Fe were distributed in bottom ash particles smaller than 5 mm. Similarly, 46.6–79.7 wt.% of Cu and 42.9–74.2 wt.% of Zn were concentrated in particles smaller than 3 mm. The Fe in the bottom ash mainly existed as hematite, and its chemical speciation was considered to limit the recovery efficiency of magnetic separation. 相似文献
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利用回转窑焚烧废物简述 总被引:2,自引:0,他引:2
本文介绍了回转窑的类型、结构和及其工艺特点,并对国内外利用回转窑焚烧危险废物的实验情况进行了综述,为我国废物焚烧领域的工作者提供借鉴。 相似文献
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Increase of sewage sludge (SS) has led to the construction of more incineration plants, exacerbating to the production of SS incineration residues. However, few studies have considered the mass balance of elements in large-scale SS incineration plants, affecting the residues treatment and utilization. In this study, flow analysis was conducted for major and trace elements in the SS, the fly ash (sewage sludge ash, SSA) and bottom ash from two large-scale SS incineration plants. The elemental characteristics were compared with those of coal fly ash (CFA), and air pollution control residues from municipal solid waste incineration (MSWIA), as well as related criteria. The results showed that the most abundant major element in SSA was Si, ranging from 120 to 240 g/kg, followed by Al (76–348 g/kg), Ca (26–113 g/kg), Fe (35–80 g/kg), and P (26–104 g/kg), and the trace elements were mainly Zn, Ba, Cu, and Mn. Not all the major elements were derived from SS. Most trace elements in the SS incineration residues accounted for 82.4%–127% of those from SS, indicating that SS was the main source of trace elements. The partitioning of heavy metals in the SS incineration residues showed that electrostatic precipitator ash or cyclone ash with high production rates were the major pollutant sinks. The differences in some major and trace elements could be indicators to differentiate SSA from CFA and MSWIA. Compared with related land criteria, the pollutants in SSA should not be ignored during disposal and utilization. 相似文献
167.
分析2010—2017年北京市三类典型废弃物焚烧源的废气二NFDA1英排放监测数据,计算排放因子和排放量,评估减排政策成效,并分析不同排放源达标排放时同类物分布特征异同和变化规律,探讨影响排放的重要因素。结果表明: 5家焚烧源平均排放浓度为 0.008~0.069 ng/m3(以TEQ计,下同),废气二NFDA1英排放因子为 0.027~1.7 μg/t,2016年向空气中排放的二NFDA1英量为 0.002 5~0.058 g;生活垃圾、危险废物和医疗废物焚烧源的低、高氯代同类物质量分数比的平均值分别为接近于 0.5、大于0.5和小于0.5,危险废物焚烧源的 ∑PCDFs、∑PCDDs质量分数比的平均值大于2; 123478-HxCDF和123678-HxCDF质量浓度接近且线性相关,具有相近的生成机理和去除效率; I-TEQ变化趋势与∑PCDFs质量分数的变化趋势基本一致,活性炭喷射和布袋除尘的去除效率是影响二NFDA1英排放的重要因素之一;危险废物焚烧源HWI1随运行时间增加排放浓度增加,而及时更换烟道管壁有助于消除“记忆效应”的不良影响。 相似文献
168.
生活垃圾焚烧发电厂周边环境二噁英污染水平及人群暴露评估 总被引:1,自引:0,他引:1
选取某典型生活垃圾焚烧发电厂为研究对象,监测其周边环境空气、土壤、地下水、农作物等环境介质中二噁英的浓度水平,初步评估周边人群二噁英暴露水平。研究结果表明,该厂周边环境空气、土壤、地下水中二噁英测定值分别为0. 236 pg TEQ/m3~0. 331 pg TEQ/m3、1. 94 ng TEQ/kg~2. 71 ng TEQ/kg、0. 17 pg TEQ/L~0. 26 pg TEQ/L,企业排放的二噁英对周边环境影响较小;成人和儿童在暴露介质中摄入二噁英总量分别为0. 959 pg TEQ/(kg·d)和1. 59 pg TEQ/(kg·d),均低于4 pg TEQ/(kg·d)的标准,经大米和面粉摄入二噁英的量超过总暴露量的90%,提示食物是人群二噁英暴露的主要介质。 相似文献
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170.