首页> 外文会议>International Conference on Combustion, Incineration/Pyrolysis and Emission Control(3rd i-CIPEC); 20041021-23; Hangzhou(CN) >Dioxins/Furans Distribution in the Unit Processes of Heat Exchangers and Bag Filters of Waste Incinerator System
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Dioxins/Furans Distribution in the Unit Processes of Heat Exchangers and Bag Filters of Waste Incinerator System

机译:废物焚化炉系统的换热器和袋式除尘器单元过程中的二恶英/呋喃分布

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Despite various studies, PCDDs/DFs behavior in MSWIs has been not well estimated because of complicated factors (operating conditions of incinerator, waste composition and flue gas treatment facilities). In this research, characteristic of dioxins behavior was investigated at unit processes after the boiler of MSWIs incinerator. In order to know PCDDs/DFs behavior, it is necessary to analyze experimental conditions of treatment facilities (temperature, flue gas flow rate, etc.) and incinerator operating conditions(furnace temperature, waste feeding rate, combustion gas flow rate, etc.) as well as the concentration of other air pollutants(SOx, NOx, CO, etc.) during PCDDs/DFs sampling period. The facilities were composed of Boiler for recovering heat, Cooling tower for decreasing temperature and Bag Filter for filtering Fly Ash, removing PCDDs/DFs and Acid Gas by injecting Activated Carbon + Ca(OH)_2. Flue gas was sampled at Boiler outlet, Bag Filter inlet and outlet coincidently. Ash samples were collected at Boiler, Cooling Tower, Bag Filter Hopper, respectively. The facilities were divided into two sections (Boiler + Cooling Tower, Bag Filter). Boiler and Cooling tower section showed a very similar behavior regardless of temperature variations. In contrast, PCDDs/DFs level through Bag Filter relatively increased specially in high-Chlorinated PCDDs/DFs. The result indicated that Low Chlorinated dioxins were removed in greater amount than High-Chlorinated dioxins at Bag filter section. Through Mass Balance Calculations extended over the Unit Processes, the release of PCDDs/DFs fro the incinerator had been also evaluated in terms of the total emission rate. Dioxins mass flux was calculated from concentrations measured in three solid residues of processes as well as in flue gases. In conclusion, the PCDDs/DFs concentration decreased consistently through Boiler + Cooling Tower +B/F in flue gases and increased in ashes, respectively. It would be considered that there exist some kinds of mechanism to increase PCDDs/DFs concentrations when flue gas passes both Cooling Tower and Bag Filter because of condensation and adsorption on the Fly Ash surface and memory effect.
机译:尽管进行了各种研究,但由于复杂因素(焚烧炉的运行条件,废物成分和烟气处理设施),尚未对MSWI中PCDDs / DFs的行为进行很好的估计。在这项研究中,对二恶英行为的特征进行了研究,以处理MSWIs焚化炉后的单位过程。为了了解PCDDs / DFs的行为,有必要分析处理设施的实验条件(温度,烟气流速等)和焚化炉的运行条件(炉温,废物进料速度,燃烧气体流速等)。以及PCDDs / DFs采样期间其他空气污染物(SOx,NOx,CO等)的浓度。这些设施包括用于回收热量的锅炉,用于降低温度的冷却塔以及用于过滤粉煤灰,通过注入活性炭+ Ca(OH)_2去除PCDDs / DF和酸性气体的布袋除尘器。烟气在锅炉出口,布袋除尘器入口和出口同时采样。灰分样品分别在锅炉,冷却塔,布袋除尘器斗中收集。设施分为两个部分(锅炉+冷却塔,布袋除尘器)。无论温度如何变化,锅炉和冷却塔的截面都表现出非常相似的行为。相反,通过袋式除尘器的PCDD / DF含量相对增加,特别是在高氯化PCDD / DF中。结果表明,在袋式除尘器部分,低氯代二恶英的去除量大于高氯代二恶英。通过扩展到单位过程的质量平衡计算,还根据总排放率评估了焚化炉中PCDDs / DFs的释放。二恶英的质量通量是根据过程中三个固体残渣以及烟道气中测得的浓度计算得出的。总之,通过锅炉+冷却塔+ B / F烟道气中PCDDs / DFs浓度持续降低,而灰烬中PCDDs / DFs浓度持续升高。人们认为,由于烟气在粉煤灰表面的凝结和吸附以及记忆效应,当烟气同时通过冷却塔和布袋除尘器时,存在某种增加PCDDs / DFs浓度的机制。

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