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Measurement and modelling of gaseous elemental iodine (I_2) dry deposition velocity on grass in the environment

机译:气体元素碘(I_2)对环境草地干沉积速度的测量与建模

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Assessing the impact of radioactive iodine on humans subsequent to a nuclear accident requires a better understanding of its behaviour in the environment. An original approach aimed at developing a model constrained by data collected during experimental campaigns has been developed. These experimental campaigns, named MIOSEC 2 and MIOSEC 3 respectively, were conducted in the middle of grassland. They are based on emissions of gaseous elemental iodine (I-2) into the atmosphere above the grassland to determine the dry deposition velocities of iodine on the grass and to model these velocities as a function of the environmental conditions, particularly wind friction velocity, sensible heat flux, and stomatal resistance. The measured dry deposition velocities were between 0.02 and 0.49 cm s(-1) during MIOSEC 2, varying by more than one order of magnitude, and between 0.48 and 1.25 cm s(-1) during MIOSEC 3. The dry deposition model for iodine developed as a result of these experiments relies on the micrometeorological characteristics of the atmospheric surface layer, the pertinent physical and chemical properties of the iodine and the surface properties of the grass; all these parameters were measured at the time of the experiments. Given the experimental conditions, the modelled dry deposition velocities varied between 0.11 and 0.51 cm s(-1) during MIOSEC 2 and between 0.31 and 1.6 cm s(-1) during MIOSEC 3. The dry deposition model for iodine indicates that the variations in deposition velocity are induced by the mechanical turbulence, since there is significant correlation between the dry deposition velocities of iodine and the wind friction velocities on grass. The model also shows that the higher deposition velocity values during MIOSEC 3 are due to the fact that the stomata were more open during the experiments. There is also significant correlation between the experimental results and modelled values both for MIOSEC 2 (R-2 = 0.61) and for MIOSEC 3 (R-2 = 0.71).
机译:评估核事故后放射性碘对人类的影响需要更好地了解其在环境中的行为。已经制定了一种原始方法,旨在开发由在实验活动期间收集的数据限制的模型。这些实验活动分别在草原中间进行了名为MioSec 2和MioSec 3。它们基于气体元素碘(I-2)的排放到草地上方的大气中,以确定草地上碘的干燥沉积速度,并以环境条件的函数,特别是风摩擦速度,明智的方式模拟这些速度热通量,气孔抗性。在MIESEC 2期间,测得的干沉积速度在0.02和0.49cm S(-1)之间,在MISEC 3期间,在0.48和1.25cm S(-1)之间的0.48和1.25cm S(-1)之间。碘的干沉积模型由于这些实验依赖于大气表面层的微观定理特性,因此碘的相关物理和化学性质以及草的表面性质;在实验时测量所有这些参数。考虑到实验条件,在MIESEC 2期间,在MIESEC 2和0.31和1.6cm S(-1)期间,模拟的干沉积速度在MISEC 3期间的0.11和1.6cm S(-1)之间变化。碘的干沉积模型表明变化沉积速度由机械湍流引起,因为碘的干沉积速度与草上的风摩擦速度之间存在显着相关性。该模型还表明,MISEC 3期间的较高沉积速度值是由于在实验期间气孔更加开放的事实。对于MIOSEC 2(R-2 = 0.61)和MIOSEC 3(R-2 = 0.71),还存在显着的相关性。

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