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Detailed source term estimation of the atmospheric release for the Fukushima Daiichi Nuclear Power Station accident by coupling simulations of an atmospheric dispersion model with an improved deposition scheme and oceanic dispersion model

机译:通过将大气弥散模型与改进的沉积方案和海洋弥散模型相结合,对福岛第一核电站事故的大气释放进行详细的源项估算

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Temporal variations in the amount of radionuclides released into the atmosphere during the Fukushima Daiichi Nuclear Power Station (FNPS1) accident and their atmospheric and marine dispersion are essential to evaluate the environmental impacts and resultant radiological doses to the public. In this paper, we estimate the detailed atmospheric releases during the accident using a reverse estimation method which calculates the release rates of radionuclides by comparing measurements of air concentration of a radionuclide or its dose rate in the environment with the ones calculated by atmospheric and oceanic transport, dispersion and deposition models. The atmospheric and oceanic models used are WSPEEDI-II (Worldwide version of System for Prediction of Environmental Emergency Dose Information) and SEA-GEARN-FDM (Finite difference oceanic dispersion model), both developed by the authors. A sophisticated deposition scheme, which deals with dry and fog-water depositions, cloud condensation nuclei (CCN) activation, and subsequent wet scavenging due to mixed-phase cloud microphysics (in-cloud scavenging) for radioactive iodine gas (I-2 and CH3I) and other particles (CsI, Cs, and Te), was incorporated into WSPEEDI-II to improve the surface deposition calculations. The results revealed that the major releases of radionuclides due to the FNPS1 accident occurred in the following periods during March 2011: the afternoon of 12 March due to the wet venting and hydrogen explosion at Unit 1, midnight of 14 March when the SRV (safety relief valve) was opened three times at Unit 2, the morning and night of 15 March, and the morning of 16 March. According to the simulation results, the highest radioactive contamination areas around FNPS1 were created from 15 to 16 March by complicated interactions among rainfall, plume movements, and the temporal variation of release rates. The simulation by WSPEEDI-II using the new source term reproduced the local and regional patterns of cumulative surface deposition of total I-131 and Cs-137 and air dose rate obtained by airborne surveys. The new source term was also tested using three atmospheric dispersion models (Modele Lagrangien de Dispersion de Particules d'ordre zero: MLDP0, Hybrid Single Particle Lagrangian Integrated Trajectory Model: HYSPLIT, and Met Office's Numerical Atmospheric-dispersion Modelling Environment: NAME) for regional and global calculations, and the calculated results showed good agreement with observed air concentration and surface deposition of Cs-137 in eastern Japan.
机译:福岛第一核电站事故(FNPS1)事故期间释放到大气中的放射性核素的时间变化及其在大气和海洋中的扩散对于评估环境影响和对公众的放射剂量至关重要。在本文中,我们使用一种反向估算方法估算事故期间的详细大气释放量,该方法通过将放射性核素的空气浓度或其在环境中的剂量率的测量值与通过大气和海洋运输所计算出的值进行比较,从而计算放射性核素的释放率,分散和沉积模型。作者使用的大气和海洋模型是WSPEEDI-II(环境应急剂量信息预测系统的全球版本)和SEA-GEARN-FDM(有限差分海洋扩散模型)。一种复杂的沉积方案,涉及干燥和雾水沉积,云凝结核(CCN)活化以及由于放射性碘气体(I-2和CH3I)的混合相云微观物理学(云中清除)而导致的后续湿清除)和其他粒子(CsI,Cs和Te),已合并到WSPEEDI-II中以改善表面沉积计算。结果显示,FNPS1事故造成的放射性核素主要释放发生在2011年3月的以下时期:3月12日下午,由于3月14日午夜SRV(安全救济)第1号机组的湿式通风和氢气爆炸3月15日的早晚和3月16日的早上,在2号单元中打开了3次)。根据模拟结果,由于降雨,羽流运动和释放速率的时间变化之间的复杂相互作用,3月15日至16日在FNPS1附近形成了最高的放射性污染区。 WSPEEDI-II使用新的源术语进行的模拟再现了总I-131和Cs-137的累积表面沉积的局部和区域模式以及通过机载测量获得的空气剂量率。新的源项还使用三个大气扩散模型(零拉格朗日粒子模型:MLDP0,混合单粒子拉格朗日综合轨迹模型:HYSPLIT和Met Office的数值大气扩散模型环境:NAME)进行了测试和全球计算,计算结果与日本东部观测到的空气浓度和Cs-137的表面沉积情况吻合良好。

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