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Gas Phase Reactions of Organic Iodine in Containment Conditions

机译:封闭条件下有机碘的气相反应

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In case of a hypothetical severe accident it is very likely that iodine at least partly deposits on painted walls of a reactor containment building. Iodine may react with painted surfaces to form organic iodine species. These organic species are a possible source of volatile iodine, which may increase the fraction of releasable iodine. Therefore, it is important to study the transport of organic iodine in containment conditions. Another question is, in which form are the organic iodides transported as gaseous molecules or as aerosol particles resulting from organic iodides reacting with radiolysis products. To answer this last question methyl iodide was fed into the EXSI facility in an air mixture. In some experiments the flow contained also humidity. The reactions took place in a quartz tube heated either to 50°C, 90°C or 120°C. UV-light was used as a source of radiation to produce ozone from oxygen. A separate generator was also applied to reach higher ozone concentrations. Nucleated aerosol particles were collected on plane filters and gaseous iodine species were trapped in trapping bottles. Aerosol mass flow rate and size distribution as well as speciation of gaseous reaction products were measured with several on-line instruments. Collected aerosol particles were analysed with SEM. It was found that the formation of aerosol particles was very fast when ozone and methyl iodide were present in the facility. Even a very low concentration of ozone produced high number concentration of particles. The measured aerosol mass concentration increased with increasing temperature and ozone concentration. Because the particle diameter was quite small (<180 nm), their settling velocity is low. Therefore, iodine containing aerosols may exist in containment atmosphere for a long period of time. Part of methyl iodide was always transported through the facility regardless of experimental conditions. All ozone was consumed in the reactions when only UV-light was used as its source. With a separate generator, ozone concentration was sufficiently high to be detected at the outlet of the facility and thus enabling the study of the reaction kinetics. The transported fractions for both methyl iodide and ozone decreased with increasing reaction temperature. The main gaseous reaction products were methanol and formaldehyde. Especially at elevated temperature other reaction products, such as formic acid and methyl formate, became important as well.
机译:如果发生假设性的严重事故,极有可能碘至少部分沉积在反应堆安全壳建筑物的粉刷墙壁上。碘可能与涂漆的表面反应形成有机碘。这些有机物质可能是挥发性碘的来源,可能会增加可释放碘的比例。因此,研究围堵条件下有机碘的运输很重要。另一个问题是,有机碘化物以哪种形式以气态分子或气溶胶颗粒的形式运输,而这种形式是由有机碘化物与辐射分解产物反应而产生的。为了回答最后一个问题,将碘甲烷以空气混合物的形式送入EXSI设备。在某些实验中,流量还包含湿度。反应在加热到50℃,90℃或120℃的石英管中进行。紫外线被用作从氧气中产生臭氧的辐射源。还使用了一个单独的发生器来达到更高的臭氧浓度。将有核气溶胶颗粒收集在平面过滤器上,并将气态碘物质捕集到捕集瓶中。使用几种在线仪器测量气溶胶质量流量和大小分布以及气态反应产物的形态。用SEM分析收集的气溶胶颗粒。发现当设施中存在臭氧和甲基碘时,气溶胶颗粒的形成非常快。即使是非常低浓度的臭氧,也会产生高浓度的颗粒。测得的气溶胶质量浓度随温度和臭氧浓度的增加而增加。由于粒径非常小(<180 nm),因此沉降速度较低。因此,含碘的气溶胶可能会在密闭气氛中长期存在。无论实验条件如何,始终将一部分甲基碘运输通过该设施。当仅使用紫外线作为光源时,反应中所有的臭氧都被消耗掉了。使用单独的发生器,臭氧浓度足够高,可以在设备的出口处检测到,因此可以研究反​​应动力学。甲基碘和臭氧的传输级分随反应温度的升高而降低。主要的气态反应产物是甲醇和甲醛。特别是在升高的温度下,其他反应产物,例如甲酸和甲酸甲酯也变得重要。

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