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Figure A.1. Variation of the detection efficiency with the distance for different age voxel phantoms and four detection systems (NOTE: Some measurement distances cannot be simulated because of the geometry of the detector and the phantom). 

Figure A.1. Variation of the detection efficiency with the distance for different age voxel phantoms and four detection systems (NOTE: Some measurement distances cannot be simulated because of the geometry of the detector and the phantom). 

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Technical Report
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DESCRIPTION This report gives technical guidelines for radio-iodine monitoring following a nuclear incident. Monitoring aspects addressed include the choice of detectors, the calibration and measurement process, factors affecting measurements, measurement uncertainties, the preparation of equipment and measurement locations, the measurement time, t...

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... From the figure, the apparent to true thyroid dose ratio on the 7th (14th) day after intake was 0.81 (0.76) in the case of exposure 24 h after the shutdown and 0.91 (0.90) in the case of exposure 72 h after the shutdown. These values would be reasonable for exposure in the postvessel melt-through phase when the release fractions of iodine and tellurium are similar to each other (21) . The radioactivity ratios of iodine isotopes and 132 Te for the Fukushima Daiichi nuclear power plant (Table 1) were also similar to those for a typical inventory in the core of a light water reactor (22) . ...
Article
In a nuclear emergency, one of the actions taken for the sake of public is to monitor thyroid exposure to radioiodines. Japan’s Nuclear Regulation Authority recently published a report on such monitoring and proposed direct thyroid measurements with conventional NaI(Tl) survey meters (e.g. Hitachi model TCS-172) as a primary screening method. A previous study proposed screening levels (SLs) used in these simplified measurements as the net reading values of the TCS-172 device. Age-specific SLs were derived from a thyroid equivalent dose of 100 mSv due to the inhalation intake of 131I. This study addressed the possible influence of short-lived iodine isotopes other than 131I on the simplified measurements. In preparation for such measurements, the responses of the device for 132I as an ingrowth component from 132Te, 133I, 134I and 135I in the thyroid were evaluated by numerical simulations using age-specific stylized phantoms in addition to those obtained for 131I in the previous study. The radioactivity ratios of the relevant isotopes were taken from the inventory data of the Fukushima Daiichi Nuclear Power Plant. The results were used to predict the net readings of the device when 132Te-132I and 133I as well as 131I were inhaled at 24 or 72 h after the shutdown of a nuclear power plant. In these cases, the signals from 132Te-132I and 133I become undetectable a couple of days after intake, which could lead to underestimations of the thyroid dose. To estimate the thyroid dose accurately from the simplified measurements, it is necessary to identify the exact time of intake after the shutdown and the actual physiochemical property of 132Te that affects the thyroid uptake of 132I.
... The system photopeak efficiency calibration for thyroid measurements was performed using a neck phantom proposed by the Belgian Nuclear Research Centre (SCK·CEN) in the CAThyMARA intercomparison programme [11]. The neck phantom, described in detail in [3], consists of a PMMA cylinder (neck) which can host one pair of vials which simulate the thyroid lobes. ...
... After an acute inhalation, the radionuclides 132 Te, 137 Cs, 134 Cs and 103 Ru are typically distributed in the human body with no specific organ accumulation. On the contrary, all radioisotopes of iodine concentrate almost exclusively in the thyroid gland-which is positioned at the base of the front of the neck typically with an overlying tissue thickness of between 0.4 and 1.5 cm [5]-reaching a maximum about 24 h post intake. Therefore, in the event of a nuclear accident, specific whole-body and thyroid measurements are required for a correct dose assessment to members of the public. ...
... Concerning thyroid measurements, that are crucial in the case of a 131 I release from a facility producing radioisotopes for medical purposes, the use of simple portable non-spectrometric equipment, such as rate meters, offers an alternative to the preferred gamma-ray spectrometry technique [5]. In fact, since only radioiodine isotopes are retained in the thyroid gland, it is not strictly necessary to perform spectrometric measurements. ...
... Therefore the nonspectrometric equipment could be enough sensitive to be used to scan thyroids of internally exposed individuals. These instruments have the advantage of being much cheaper than more sophisticated (spectrometric) ones, readily portable and simple to operate (requiring a basic training) [5,6]. ...
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In order to properly respond to an emergency caused by an accident in a nuclear power plant with a spread of radionuclides in the atmosphere, we propose a field procedure to perform a large-scale individual thyroid monitoring of internal contamination due to inhalation of 131I, by means of non-spectrometric equipment, in particular dose rate meters. Specific attention is paid to the individual monitoring of children, because of the very high radiosensitivity of the child's thyroid to the carcinogenic effects of ionising radiation. The device performance was evaluated by measuring mock iodine sources provided in the Child and Adult Thyroid Monitoring After Reactor Accident (CAThyMARA) intercomparison and, just for a scintillator dose rate meter, by means of 60 s acquisitions of healthy volunteers' thyroids. All the devices showed a remarkable accuracy in quantification of equivalent 131I activity in the thyroids of persons of all ages. The selected scintillator dose rate meter showed detection limit values resulting in a maximum committed equivalent dose to thyroid HT, assuming an acute 131I inhalation occurred five days before the measurement, equal to 10 mSv (related to five-year-old children). Considering the level of HT values associated with the calculated detection limit activities, the proposed procedure has a significant sensitivity to be used for fast internally thyroid monitoring in nuclear or radiological emergencies, allowing daily monitoring a large amount of individuals.
Chapter
Internal monitoring of a large group of contaminated people is mandatory during nuclear and radiological emergency situations. The emergency preparedness and response will be implemented during such off-normal situations. The action plans will be based on the generic and operational criteria. Rapid monitoring results play a significant role in the decision-making. Most of the time the specialized internal contamination monitoring facilities may be far from the incident site. In such scenarios, independent internal contamination monitoring units as mobile units may be required to be set up near the affected site for primary screening of the contaminated individuals. In-vivo measurement techniques can be used for rapid screening of the public by using, field deployable in-vivo monitoring systems like Portable Whole-Body Monitor (PWBM) and Portable Thyroid Monitors (PTM), survey meters, laboratory-based Quick Scan Whole Body Monitor, etc. The present chapter briefly explains the preparedness and response strategies during nuclear or radiological emergency situations and the internal contamination monitoring protocols followed during such off-normal situations.
Chapter
It has been long known that external radiation exposure in the area of the thyroid is closely associated with an increased risk for thyroid cancer, especially in children. Initially it was not clear if the increased risk also applied to internal radiation from radioactive iodine, especially iodine-131 (¹³¹I). Any doubt about this was erased in the wake of the Chernobyl accident that led to many thyroid cancers. This cemented the universal acceptance of the need to be prepared for the possibility of future accidents and, specifically, for the use of potassium iodide to mitigate the risk. The subsequent Fukushima accident reinforced this need, but also highlighted some of the complexities. Among them was the difficulty of rapidly evaluating the magnitude of the thyroid radiation doses in order to guide officials and the population about using potassium iodide. In retrospect, the Fukushima-related doses were not high enough to advise taking potassium iodide, but it was given in some areas and not others. Across the Pacific, along the West Coast of the United States, supplies of potassium iodide were needlessly sold out, although it is not known how much was actually ingested. The goals of this chapter are to inform health care workers about potassium iodide, how to promote potassium iodide distribution in advance of a possible release of radioactive iodine into the atmosphere, and how to inform the public in the event of such a release.
Article
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