RADIATION MONITORING EXPERIMENT USING THERMOLUMINESCENT DOSIMETER FOR THE TR 19 CYCLOTRON AREA IN NUCLEAR RESEARCH INSTITUTE

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RADIATION MONITORING EXPERIMENT USING THERMOLUMINESCENT DOSIMETER FOR THE TR 19 CYCLOTRON AREA IN NUCLEAR RESEARCH INSTITUTE A. STOCHIOIU, L. CRACIUN, F. MIHAI, I. TUDOR Horia Hulubei National Institute for Nuclear Physics and Engineering,P.O.Box MG-6, RO-077125 Bucharest-Magurele, Romania E-mails: stoc@.nipne.ro; cliviu@nipne.ro; fmihai@nipne.ro; itudor@nipne.ro Abstract. The core of Radiopharmaceuticals Research Centre, CCR, is represented by a TR19 cyclotron (Advanced Cyclotron Systems Inc.), a versatile and fully automated and computer controlled machine. This cyclotron accelerates negative ions (H - ), on a vertically arranged plane, up to 19 MeV energy, and is provided with two external beam lines and dual extraction capabilities. The main use is for the production of positron emitting radionuclide namely 18 F, 15 O, 13 N and 11 C. The pharmaceuticals labeled with these radioisotopes are used for positron emission tomography (PET) imaging. The radiation levels were measured in the facility at different locations namely cyclotron vault, control console, radiochemistry laboratory, beam extension room and the stack using a comprehensive computerized monitoring system. The thermoluminescent dosimeter, TLD, LiF: Mg, Cu, P are commonly used for the radiation dose measurements to determine the ambient dose equivalent, which are part of passive systems of environmental radioactivity monitoring. In this work TLD were distributed for a period of 87 days in 12 points of interest according to the map of the cyclotron area and were read out to determine the corresponding activities. All measured values were higher than those obtained in IFIN- HH nuclear research units so, at cyclotron vault point the ambient dose equivalent rate was 56 695 nsv/h. Key words: Radiation measurements, thermoluminescent dosimeter, TR19 cyclotron 1. INTRODUCTION In year 2012 IFIN-HH has implemented the investment project CCR (Radiopharmaceuticals Research Centre) dedicated to the study of radiopharmaceuticals, both for medical imaging and targeted therapy, in view of their future implementation in medical practice. The project consists of a more than 1330 m² state-of-the-art center comprising one of the newest generation of cyclotrons (TR19) and a highly specialized radiopharmaceutical facility. The cyclotron has an associated radiochemistry facility that contains chemistry modules housed in adequately shielded hot cells meant for the synthesis of the pharmaceuticals labeled with these positron emitters [1] During cyclotron operation, some radioactive nuclides are produced by beam activation of the cyclotron materials and surrounded air molecules. The activity varies from place to place inside the cyclotron room and some radioactivity values could be remarkable in the places outside the cyclotron room, in the working area. Concerning with norms and laws [2, 3] in force the CCR activity requires the monitoring and assessment of the environmental radioactivity level. In this way,

2 the CCR has a comprehensive computerized monitoring system with gamma and neutron detectors that monitories permanently all the areas from the building. Also, annually by a program of monitoring the radiation environment level is reported for Horia Hulubei, National Institute R&D of Physics and Nuclear Engineering that included beside other laboratory with nuclear activity and the CCR location. The principal aim of occupational protection and safety can be stated as the achievement and maintenance of an acceptably safe and healthy working environment. Therefore the mapping of the produced radioactivity in the cyclotron area is important for radiation protection purposes. Besides centralized radiological monitoring system, a passive system of radioactivity measuring would be necessary. In this work the radiation activity values of the CCR environment measured with SDTM thermoluminescent (TL) environment dosimetry system are presented. 2. MATERIALS AND METHODS In order to obtain the radiological mapping of the CCR studied area the thermoluminescent (TL) environment dosimetry system has been used. So, the ambient dose equivalent and its flow values have been assessed. The TLD is classified as passive dosimeter and the power supply is not required during its working period. The TLD system consists of: i) thermoluminescent detectors based on LiF: Mg, Cu, P, GR-200 type A; ii) dosimetric box with minicasete 3-7; iii) ANALYSER RA '94 TL reader. The dosimetric box from PVC (polyvinyl chloride) consists of box and lid and its closing is achieved by screwing. The minicasete from the inside of the dosimetric box are also composed of body and lid and are closing by pressing. Also, the minicasete are made from the same material as the dosimetric box Figure 1. The dosimetry box (model DMT-S) is designed and made in IFIN-HH. The thermoluminescent (TL) environment dosimetry system allows measurement of doses from 0.01 µsv to 100 msv in the 30 kev 3MeV range of energy.for ambient dose equivalent measurement the TL dosimeters were suspendedat one meter of the earth surface in studied area. The TL detector is based on thermoluminescent phenomenon induced of the ionizing radiation and the luminous radiation is emitted by their heating to the characteristic temperature typical for the each type of detector. The radiation intensity is proportional with integrated doses during the exposure period.

3 Fig.1 Dosimetry box with thermoluminescent detectors The ambient dose equivalent values have been performed take into consideration the specifically calibration standards and procedures from dosimetry laboratory [4, 5]. In order to determine the calibration factor the TL dosimeters were calibrated to a Secondary Standard Dosimetry (SSD) in the ambient dose equivalent H*(10) [msv]. In the study, 12 dosimeters box were placed within 12 locations of interest from CCR for a period of 87 days after which they were read and interpreted Figure 2.In each dosimeter box were paced 3 minicaset with TL detectors. After monitoring period the TL detectors were subtracted from minicaset with a vacuum tweezers and were read to the ANALYSER RA '94 TL reader. The ambient dose equivalent values were assessed taking into consideration the mean values obtained by the reading of the three TL detectors from each dosimetric box. In the studied period of three months only three experiments occurred in the Cyclotron vault location totaling an operating period of 40 hours. 3. RESULTS AND DISCUSSIONS Measurements performed in the 12 locations confirmed the high degree of security for workers. As it seen from the Table 1 the equivalent dose inside and outside of the irradiation area is about 118 msv for three months of monitoring and ranging from 0.219 to 0.341 msv for the this period of time. So, the annual equivalent dose in the working area varies in the range 0.876 msv to 1.023 msv. These values are below the maximum permissible dose for o occupational exposed person that is 20 msv/year [6]. The values outside of the Cyclotron vault are extremely low. The lowest level measured of 104.67 nsv/h is in the control room area where operators working throughout the experiment activity. In the Cyclotron vault location namely hot area the ambient dose equivalent rate value is 3mSv/h take into consideration only those 40 hours of experimental activity. This value is comparable with other types of cyclotrons considering the same rate of experimental operation in the hot area [7]. In the access places the dose does not exceed the background radiation level.

4 Fig.2 Schematic layout of the Radiopharmaceuticals Research Centre and the positions of the monitoring points No Table 1 Measurement values for ambient dose equivalent and its rate Location Dosimeter cod Ambient dose equivalent [msv] Ambient dose equivalent rate [nsv/h] 1 Control room 0148 0.219 ± 0.008 104.67 ± 3.99 2 Electrical room 0173 0.341 ± 0.008 163.35 ± 3.91 3 Cyclotron vault 0131 118.379 ± 46.298 56 694.80 ±273.26 4 Experimental Hall 0169 0.334 ± 0.016 159.76 ± 7.43 5 Extension of Experimental 0108 0.290 ± 0.059 138.79 ± 28.40 Hall 6 Equipment room 0091 0.285 ± 0.005 136.47 ± 2.16 7 Locker room 0079 0.337 ± 0.035 161.47 ± 16.87 8 Basement 0101 0.278 ± 0.014 133.09 ± 6.62 9 Maintenance corridor 0087 0.307 ± 0.046 147.24 ± 21.84 10 Mechanical room 3003 0.308 ± 0.050 147.35 ± 23.97 11 Room 0186 0.264 ± 0.031 126.21 ± 14.84 12 Potentially radioactive air compressing station 0137 0.275 ± 0.039 131.66 ± 18.51

5 4. CONCLUSIONS Using the TL dosimetry system for monitoring the controlled area around the TR- 19 cyclotron the ambient equivalent dose and its flow in relevant points inside and outside were recorded. The mean equivalent flow dose recorded: In the hot area the value of 3mSv/h is comparable with other types of cyclotrons; At the access points for personal the values not exceed the background level. It can be concluded that presently all workers are safe in terms of radiological; The comprehensive computerized monitoring system with gamma and neutron detectors that permanently monitories all the CCR area provides an effective solution for the control of various aspects of production and radiation safety in a medical cyclotron facility. In addition the TL dosimetry proved that the radiation levels were observed to be well below the permissible limits. REFERENCES 1. I. Ursu, L. Craciun, D. Niculae, N.V. Zamfir. Rom. J. Phys. 58 (9 10), 1327 1336 (2013). 2. Law no. 111/1996 on the safe deployment regulation authorization and control of nuclear activities. Revision 2 (2000) Bucharest. Romania. 3. NSR-01 2002 Fundamental Norms of Radiological Safety. National Commission for Nuclear Activities Control. Bucharest. Romania. 4. ISO/IEC 17025 (2005) General requirements for the competence of testing and calibration laboratories. International Standard Organization/ International Electronical Commission. 5. CEI-IEC 61066 Thermoluminescence dosimetry systems for personal and environmental monitoring (2006). 6. NSR-06 (2002). Norms on Radiological Safety. Norms of individual dosimetry. National Commission for Nuclear Activities Control, Bucharest, Romania. 7. A.A. Alharbi. Princess Nora University. Riyadh. Saudi Arabia.(2011)