applied sciences
Article Integrated and Portable Probe Based on Functional Plastic Scintillator for Detection of Radioactive Cesium
Sujung Min 1,2, Hara Kang 1, Bumkyung Seo 1, Changhyun Roh 1,3,* , Sangbum Hong 1,* and Jaehak Cheong 2,*
1 Decommissioning Technology Research Division, Korea Atomic Energy Research Institute, Daejeon 34057, Korea; [email protected] (S.M.); [email protected] (H.K.); [email protected] (B.S.) 2 Department of Nuclear Engineering, Kyung-Hee University, Yongin-si 17104, Gyeonggi-do, Korea 3 Quantum Energy Chemical Engineering, University of Science and Technology (UST), 217 Gajeong-ro, Daejeon 34113, Korea * Correspondence: [email protected] (C.R.); [email protected] (S.H.); [email protected] (J.C.)
Abstract: The highly reliable and direct detection of radioactive cesium has gained potential interest due to in-situ detection and monitoring in environments. In this study, we elucidated an integrated and portable probe based on functional plastic scintillator for detection of radioactive cesium. A functional plastic scintillator with improved detection efficiency was fabricated including CdTe (cad- mium telluride) material. Monolith-typed functional plastic scintillator having a diameter of 50 mm and a thickness of 30 mm was manufactured by adding 2,5-diphenyloxazole (PPO, 0.4 wt%), 1,4 di[2-(5phenyloxazolyl)]benzene (POPOP, 0.01 wt%), and CdTe (0.2 wt%) materials in a styrene-based matrix. To evaluate the applicability of the plastic scintillator manufactured to in-situ radiological measurement, an integrated plastic detection system was created, and the measurement experiment was performed using the Cs-137 radiation source. Additionally, detection efficiency was compared with a commercial plastic scintillator. As results, the efficiency and light yield of a functional plastic Citation: Min, S.; Kang, H.; Seo, B.; scintillator including CdTe were higher than a commercial plastic scintillator. Furthermore, the Roh, C.; Hong, S.; Cheong, J. Integrated and Portable Probe Based remarkable performance of the functional plastic scintillator was confirmed through comparative on Functional Plastic Scintillator for analysis with Monte Carlo simulation. Detection of Radioactive Cesium. Appl. Sci. 2021, 11, 5210. https:// Keywords: detection; integrated portable probe; Cs-137; plastic scintillator; simulation doi.org/10.3390/app11115210
Academic Editor: Antonio Di Bartolomeo 1. Introduction In general, it is necessary to develop residual radioactivity measurement technology Received: 10 May 2021 that can easily access the site, and the technology in radiological measurements that can Accepted: 2 June 2021 safely and effectively evaluate the environment, contaminated by a nuclear safeguard or Published: 4 June 2021 serious accident at a nuclear facility [1–7]. In addition, there must be verified that the site is not contaminated for reuse of the site after the nuclear facilities are dismantled. Until now, Publisher’s Note: MDPI stays neutral a lot of studies have been conducted to secure technologies that can prepare for serious with regard to jurisdictional claims in accidents such as Chernobyl and Fukushima [7–13]. The total amount of radioactivity published maps and institutional affil- emitted by the Chernobyl accident was about 12 × 1018 Bq [14]. The behavior of radioactive iations. particles largely depends on diffusion factor, particle size, and rainfall, and large particles such as nuclear fuel dust were mostly deposited within 100 km radius of the reactor [13]. In the Chernobyl nuclear accident, radioactive Cs-137 from one of the fission products of U-235 contaminated about 125,000 km2 in Belarus, Ukraine, and Western Russia with a Copyright: © 2021 by the authors. concentration of 37 kBq/m2 [13]. In the Fukushima accident, a large area was contaminated Licensee MDPI, Basel, Switzerland. by the radioactive elements, and one of the major contaminated radionuclides was analyzed This article is an open access article as a Cs-137 [12,13]. Additionally, Cs-137 was easily released from the nuclear power plant distributed under the terms and accident and was rapidly spread to the environments as a mobile element. The decay conditions of the Creative Commons Attribution (CC BY) license (https:// diagram and probability of Cs-137 were shown in Figure1 and Table1. Most of Cs-137 creativecommons.org/licenses/by/ decays to Ba-137 and then gamma decays to a stable state at 0.662 MeV. There are two − − 4.0/). β decay channels. First, 94.6% of β decays proceed from Cs-137 to the excited state
Appl. Sci. 2021, 11, 5210. https://doi.org/10.3390/app11115210 https://www.mdpi.com/journal/applsci Appl.Appl. Sci. Sci. 20212021, 11, 11, ,x 5210 FOR PEER REVIEW 2 of 15 2 of 15
ofmetastable Ba-137m withstate maximumthat decays electron with a 2.552 energy min of 0.514half-life MeV. to the The ground Ba-137m state is a of metastable Ba-137 with emis- state that decays with a 2.552 min half-life to the ground state of Ba-137 with emission of a sion of a 0.662 MeV gamma ray photon. Second, 5.4% of β− decay proceeds directly from Cs- 0.662 MeV gamma ray photon. Second, 5.4% of β− decay proceeds directly from Cs-137 137 to the ground state of Ba-137 with maximum electron energy of 1.176 MeV. Cs-137 has a to the ground state of Ba-137 with maximum electron energy of 1.176 MeV. Cs-137 has ahalf-life half-life of of 30.17 30.17 ±± 0.030.03 years years [15], [15], which cancan causecause long-termlong-term damage damage when when exposed exposed to the toenvironment the environment [16–25]. [16– Cesium25]. Cesium has hassimilar similar chemical chemical properties properties to topotassium potassium (K), (K), so so it is easily itconcentrated is easily concentrated in crops such in crops as rice. such In as addition, rice. In addition,it occupies it occupiesa large amount a large of amount artificial of radioac- artificialtive gamma-emitting radioactive gamma-emitting isotopes that isotopeshave been that leaked have been through leaked nuclear through tests nuclear and testsnuclear acci- anddents. nuclear In this accidents. regard, cesium In this regard,is an important cesium is radionuclide an important for radionuclide detection and for detectionmonitoring in en- andvironments monitoring and in contaminated environments sites. and contaminated sites.
Figure 1. Decay of diagram of 137Cs. Figure 1. Decay of diagram of 137Cs.
Table 1. β− decay process, electron energy, and probability of Cs-137. Table 1. β− decay process, electron energy, and probability of Cs-137. 137 Cs (Ek)max (Ek)avg (Eγ) Probability 137Cs (Ek)max (Ek)avg (Eγ) Probability − 1 β decay− 0.514 MeV 0.170 MeV - 94.6% ① − β decay 0.514 MeV 0.170 MeV - 94.6% 2 β decay 1.176 MeV 0.420 MeV - 5.4% ② − Internal conversionβ decay 1.176 MeV 0.420 MeV - 5.4% 3 - - - 7.8% ③ Internal(K shell)conversion (K shell) - - - 7.8% Internal conversion Internal conversion (L, M shell)------1.80% 1.80% ④ (L, M shell)γ decay - - 0.662 MeV 85% 4 γ decay - - 0.662 MeV 85% Plastic detectors are widely used as large size detectors. Additionally, over the past few decades,Plastic many detectors studies are widelyhave been used conducted as large size on detectors. plastic scintillators Additionally, composed over the past of polymer few decades, many studies have been conducted on plastic scintillators composed of matrix containing nanomaterials as an alternative to conventional inorganic scintillators polymer matrix containing nanomaterials as an alternative to conventional inorganic scintillators[26]. Plastic [26 scintillators]. Plastic scintillators are generally are generally manufa manufacturedctured by thermal by thermal polyme polymerization,rization, doping, or doping,coating orby coating adding by materials adding materials such as fluorescent such as fluorescent dye. However, dye. However, direct mixing direct mixing of nanomateri- ofals nanomaterials and polymers and is polymersless efficient is less in efficientproduc ining producing transparent transparent nanocomposites. nanocomposites. Because nano- Becausematerials nanomaterials tend to aggregate tend to due aggregate to their due high to their specific high surface specific surfacearea and area surface and surface energy, trans- energy,parency transparency is lost by Rayleigh is lost by Rayleighscattering. scattering. To increase To increase the transparency, the transparency, research research is required is to requiredreduce the to reduce aggregation the aggregation of nanomaterials of nanomaterials [27]. [The27]. Theplastic plastic detector detector is iscomposed composed of a low ofatomic a low number atomic numbermaterial material such as suchC, H, as O, C, so H, its O, accuracy so its accuracy is low due is low to low due stopping to low power stopping power and light yield. Because of these properties, plastic scintillators are used in and light yield. Because of these properties, plastic scintillators are used in applications such applications such as fast neutron detection, charged particle tracking, and non-destructive testing.as fast neutron Plastic scintillators detection, have charged advantages particle over tracking, inorganic and scintillators non-destructive such as fastertesting. decay Plastic scin- timetillators (about have 10 ns),advantages non-hygroscopicity, over inorganic relatively scintilla lowtors manufacturing such as faster cost, decay robustness, time (about and 10 ns), processability.non-hygroscopicity, Using these relatively advantages, low manufacturing it is possible to cost, develop robustness, a plasticscintillator and processability. with Us- improveding these detectionadvantages, efficiency it is possible by adding to develop nanomaterials a plastic of scintillator high atomic with number improved to the detection plasticefficiency matrix by [adding28–36]. nanomaterials of high atomic number to the plastic matrix [28–36]. InIn general, general, Monte Monte Carlo Carlo codes codes are are widely widely used used for radiationfor radiation instrument instrument design, design, per- perfor- formancemance evaluation evaluation of ofprototypes, prototypes, and and detector detector calibration calibration [37–40]. [37–40 The]. The performance performance of the com- mercial plastic and the CdTe-loaded plastic scintillator was verified through the MCNP sim- ulation. MCNP is a relatively accurate evaluation method for solving a three-dimensional transport equation. In the Monte Carlo method, the spatial structure is simulated exactly as the actual structure and the reaction cross-sectional area is used as a continuous function of energy. Appl. Sci. 2021, 11, 5210 3 of 15
of the commercial plastic and the CdTe-loaded plastic scintillator was verified through the MCNP simulation. MCNP is a relatively accurate evaluation method for solving a three-dimensional transport equation. In the Monte Carlo method, the spatial structure is Appl. Sci. 2021, 11, x FOR PEER REVIEWsimulated exactly as the actual structure and the reaction cross-sectional area is used3 asof 15 a continuous function of energy. In this study, we elucidated an integrated and portable probe based on a functional plastic scintillator for detection of radioactive cesium. In addition, the results were com- paredIn and this analyzed study, we with elucidated the results an ofintegrat the MCNPed and simulation. portable probe based on a functional plastic scintillator for detection of radioactive cesium. In addition, the results were com- 2.pared Materials and analyzed and Methods with the results of the MCNP simulation. 2.1. Chemicals 2. Materials and Methods All chemicals and reagents were commercial products. Styrene (99.9%), 2,5- Diphenyloxazole2.1. Chemicals (PPO, >95%), 1,4-bis(5-phenyloxazol-2-yl) benzene (POPOP, >95%), and CdTeAll used chemicals were purchased and reagents from were Sigma-Aldrich commercial(St. products. Louis, Styrene MO, USA) (99.9%), on a 2,5-Diphe- technical puritynyloxazole grade. (PPO, >95%), 1,4-bis(5-phenyloxazol-2-yl) benzene (POPOP, >95%), and CdTe used were purchased from Sigma-Aldrich (St. Louis, MO, USA) on a technical purity grade. 2.2. Fabrication of a Functional Plastic Scintillator 2.2. FabricationA styrene-based of a Func plastictional scintillator Plastic Scintillator was fabricated by a polymerization method, and its performanceA styrene-based was comparedplastic scintillator and analyzed was fabricated with a PVT-basedby a polymerization commercial method, scintillator and its (EJ-200).performance Plastics was werecompared manufactured and analyzed by the with process a PVT-based shown incommercial Figure2. The scintillator materials (EJ-200). used inPlastics the manufacture were manufactured of plastics by werethe process styrene, show PPOn in (2,5-diphenyloxazole), Figure 2. The materials POPOP used in (1,4the man- di[2- (5phenyloxazolyl)]benzene),ufacture of plastics were styrene, CdTe, PPO and (2,5 plastics-diphenyloxazole), with a diameter POPOP of 50 mm (1,4 anddi[2-(5phenyloxa- a thickness of 30 mm. Styrene was used as the primary solvent, PPO was used as the primary fluorophore, zolyl)]benzene), CdTe, and plastics with a diameter of 50 mm and a thickness of 30 mm. Sty- and POPOP was used as the secondary fluorophore. Although the types of nanomaterials rene was used as the primary solvent, PPO was used as the primary fluorophore, and POPOP are various, CdTe was used. The contents (wt%) of organic dye and CdTe were selected was used as the secondary fluorophore. Although the types of nanomaterials are various, due to previous studies [31]. The amounts of materials added to the styrene were PPO CdTe was used. The contents (wt%) of organic dye and CdTe were selected due to previous (0.4 wt%), POPOP (0.01 wt%), and nanomaterials (0.2 wt%). The plastic scintillator used studies [31]. The amounts of materials added to the styrene were PPO (0.4 wt%), POPOP (0.01 styrene as a basic matrix material, and a nanomaterial having an emission wavelength wt%), and nanomaterials (0.2 wt%). The plastic scintillator used styrene as a basic matrix ma- range of 500–600 nm was selected. CdTe nanomaterial was mixed with the matrix material, terial, and a nanomaterial having an emission wavelength range of 500–600 nm was selected. and stirred at 60 ◦C. After the stirring process for about 2–3 h was completed, the weight CdTe nanomaterial was mixed with the matrix material, and stirred at 60 °C. After the stirring suitable for the thickness of the plastic was measured. The sample was placed in a vial for process for about 2–3 h was completed, the weight suitable for the thickness of the plastic was polymerization and fine bubbles generated during stirring were removed. Fine bubbles measured. The sample was placed in a vial for polymerization and fine bubbles generated can cause cracking due to internal stress during the polymerization process, and since itduring reduces stirring optical were properties. removed. Fine Bubble bubbles removal can cause process cracking of about due 1–2to internal h is required. stress during The de-bubbledthe polymerization sample process, is polymerized and since init reduce a vacuums optical oven properties. at a temperature Bubble removal of up toprocess 120 ◦ C.of Atabout this 1–2 time, h is it required. is important The tode-bubbled increase thesample temperature is polymerized slowly, in and a vacuum if the temperature oven at a tem- is increasedperature of rapidly, up to 120 bubbles °C. At in this the time, sample it is mayimportant be regenerated. to increase The the polymerizationtemperature slowly, process and takesif the abouttemperature 70 h. Plastics is increased that have rapidly, gone throughbubbles in the the polymerization sample may processbe regenerated. are finished The afterpolymerization cutting and process polishing takes the about surface 70 h. to Plastics increase that the have transmittance. gone through the polymerization process are finished after cutting and polishing the surface to increase the transmittance.
FigureFigure 2.2. ManufacturingManufacturing processprocess ofof aa functionalfunctional plasticplastic scintillator.scintillator.
2.3. MCNP Simulation Monte Carlo simulation is a method for solving problems of physical and mathemat- ical systems by generating random numbers and using a probabilistic model. The MCNP code can construct various geometry through the cell card. After modeling the actual ge- ometry through the MCNP computational simulation, the spectrum of the energy accu- mulated in the scintillator was obtained. And, input data of surface flux in a MCNP 6 simulation was presented in Figure S1. Appl. Sci. 2021, 11, x FOR PEER REVIEW 4 of 15
Figure 3 is the result of calculating the deposited energy for each thickness using MCNP to select the plastic scintillator thickness. The energy of the incident photon is de- posited through interaction as it passes through the scintillator. Figure 3a shows the ge- ometry for computational simulation, and the Cs-137 radiation source was placed 20 mm away from the plastic surface. Figure 3b shows the flux by thickness, and Figure 3c shows the energy spectrum by thickness. In this study, a plastic scintillator was fabricated with a thickness of 30 mm showing about 70% energy deposition. Figure 4 shows the geometry for computational simulation of a plastic detector man- ufactured with a selected 30 mm thickness. The distance of the radiation source was set to 20 mm, 50 mm, and 100 mm under the same conditions as the experiment, and the gamma energy emitted from the radiation source was set to emit only a single energy of interest.
Appl. Sci. 2021Here,, 11, 5210 only one detector and one source are simulated, and the surrounding environment4 of 15 is not considered because it was not expected to have a significant impact on scattering. The size of the radiation source is 2.5 cm in diameter and the location of the source was used as a point in2.3. the MCNP simulation. Simulation It was also set up using a Gaussian energy broadening (GEB) card to obtain the ideal Monte Carlo simulation is a method for solving problems of physical and mathe- Compton spectrummatical of the systems plastic by generatingscintillator. random As the numbers parameters and usingfor GEB a probabilistic in Equation model. (1), The values of a, b, andMCNP c were code applied can construct as 0.00093789, various geometry 0.00498, throughand −0.05999, the cell respectively. card. After modeling And, the all input data of actualenergy geometry spectrum through were the presented MCNP computational in Figure S2. simulation, the spectrum of the energy accumulated in the scintillator was obtained. And, input data of surface flux in a MCNP 6 simulation was presentedFWHM in Figure= a + b S1.√(E+cE2) (1) Figure3 is the result of calculating the deposited energy for each thickness using Here, FWHMMCNP means to select full width the plastic at half scintillator maximum, thickness. E means The gamma-ray energy of the energy. incident photon is The spectrumdeposited derived through through interaction the MCNP as it passessimulation through was the compared scintillator. with Figure the3a actual shows the measurement spectrum,geometry and for computational since the photopeak simulation, did and not the appear Cs-137 radiation due to the source characteristics was placed 20 mm of the plastic scintillator,away from the plasticdetection surface. effi Figureciency3b was shows calculated the flux by using thickness, the andgross Figure counts.3c shows To make the statisticalthe energy uncertainty spectrum byof thickness.the calculation In this study,result a less plastic than scintillator 5%, 109 wasphotons fabricated were with a generated in eachthickness geometry of 30 to mm calculate showing the about measurement 70% energy deposition.efficiency of the plastic detector.
Figure 3. The geometry used in the MCNP computational simulation for the selection of plastic thickness (a), flux by thickness (left), configuration of geometry (right)(b), energy spectrum by thickness (c).
Figure4 shows the geometry for computational simulation of a plastic detector manu- factured with a selected 30 mm thickness. The distance of the radiation source was set to 20 mm, 50 mm, and 100 mm under the same conditions as the experiment, and the gamma energy emitted from the radiation source was set to emit only a single energy of interest. Here, only one detector and one source are simulated, and the surrounding environment is Appl. Sci. 2021, 11, 5210 5 of 15
Appl. Sci. 2021, 11, x FOR PEER REVIEW 5 of 15
not considered because it was not expected to have a significant impact on scattering. The Figuresize of 3. the The radiation geometry sourceused in isthe 2.5 MCNP cm in computational diameter and simulation the location for the of selectio the sourcen of plastic was thickness used as (aa), point flux by in thickness the simulation. (left), configuration of geometry (right) (b), energy spectrum by thickness (c).
Figure 4. Geometry for computational simulation of 30-mm-thick plastic scintillators. It was also set up using a Gaussian energy broadening (GEB) card to obtain the ideal 2.4. Manufacturing of Integrated Functional Plastic Detection System Compton spectrum of the plastic scintillator. As the parameters for GEB in Equation (1), valuesTo of evaluate a, b, and the c wereperformance applied asof 0.00093789,the CdTe-loaded 0.00498, plastic and −detector,0.05999, a respectively. plastic detection And, systemall input was data constructed of energy spectrum as shown were in Figure presented 5a. Additionally, in Figure S2. the signal generated from the plastic detector is amplified through a preamplifier√ and amplifier, and the amplified analog signal is digitized throughFWHM a multi-channel = a + b (E+cE analyzer2) and then stored. A high volt- (1) age was applied to the plastic detector so that the generated electrons were collected by the electrode.Here, FWHM The system means fullwas width constructed at half maximum,using PMT E(ET-9266KB, means gamma-ray ET-Enterprises energy. Ltd., Uxbridge,The spectrum UK), power derived supply through (DT5423, the MCNP CAEN simulation, Viareggio, was Italy), compared Preamp with (Amcrys the actual 544, Amcrysmeasurement Ltd., spectrum,Kharkiv, andUkraine), since theAmp photopeak (DT5781, did CAEN, not appear Viareggio, due to theItaly), characteristics and MCA (DT5781,of the plastic CAEN, scintillator, Viareggio, the detectionItaly). Additionally, efficiency was the calculatedplastic detector using and the grossdata processing counts. To 9 systemmake the were statistical manufactured uncertainty as an of integrated the calculation system, result so that less the than integrated 5%, 10 photonssystem can were be usedgenerated as a portable in each geometry detection tosystem calculate as shown the measurement in Figure 5b. efficiency Figure 5c of theshows plastic a schematic detector. illustration for plastic detection system. The integrated box can contain a data processing 2.4. Manufacturing of Integrated Functional Plastic Detection System system, which is custom-made using an anti-shock sponge. Additionally, it was stored in a darkTo room evaluate for about the performance 12 h after replacing of the CdTe-loaded the scintillator plastic to remove detector, the a plasticafterglow detection of the PMTsystem that was occurred constructed while asreplacing shown inthe Figure plastic5a. scintillator. Additionally, the signal generated from the plastic detector is amplified through a preamplifier and amplifier, and the amplified analog signal is digitized through a multi-channel analyzer and then stored. A high voltage was applied to the plastic detector so that the generated electrons were collected by the electrode. The system was constructed using PMT (ET-9266KB, ET-Enterprises Ltd., Uxbridge, UK), power supply (DT5423, CAEN, Viareggio, Italy), Preamp (Amcrys 544, Amcrys Ltd., Kharkiv, Ukraine), Amp (DT5781, CAEN, Viareggio, Italy), and MCA (DT5781, CAEN, Viareggio, Italy). Additionally, the plastic detector and data processing system were manufactured as an integrated system, so that the integrated system can be used as a portable detection system as shown in Figure5b. Figure5c shows a schematic illustration for plastic detection system. The integrated box can contain a data processing system, which is custom-made using an anti-shock sponge. Additionally, it was stored in a dark room for about 12 h after replacing the scintillator to remove the afterglow of the PMT that occurred while replacing the plastic scintillator. Appl.Appl. Sci. Sci. 20212021, 11, 11, x, 5210FOR PEER REVIEW 6 of6 of15 15
FigureFigure 5. 5.(a()a Real) Real picture picture of of the the performance performance experime experimentalntal setup setup for for gamma gamma energy energy spectrum spectrum using using a functional plastic scintillator. (b) Real picture of integrated device box and portable probe with a a functional plastic scintillator. (b) Real picture of integrated device box and portable probe with a functional scintillator. (c) Schematic illustration for plastic detection system. functional scintillator. (c) Schematic illustration for plastic detection system.
3.3. Results Results and and Discussion Discussion TheThe transparency transparency of of the the plastic plastic scintillator scintillator decreases decreases due due to to the the coagulation coagulation of of nano- nano- materialsmaterials with with high high surface surface energy energy and and precip precipitationitation during during the the plastic plastic polymerization polymerization process,process, which which may may adversely adversely affect affect the the optica opticall properties. properties. Therefore, Therefore, for for the the transparency transparency ofof the the plastic plastic scintillator, scintillator, it itis is necessary necessary to to be be careful careful in in the the processes processes of of stirring, stirring, bubbles bubbles removal,removal, slow slow heating, heating, slow slow cooling, cooling, and and poli polishing.shing. Figure Figure 6a6a shows shows the the transparency transparency of of thethe CdTe-loaded CdTe-loaded plastic, plastic, and and Figure Figure 6b,c6b,c show show the the UV-Vis UV-Vis absorption absorption and and PL PL emission emission spectraspectra of of the the plastic plastic scintillator. TheThe absorptionabsorption peak peak was was confirmed confirmed at at about about 250–400 250–400 nm, nm,and and 475 475 nm nm emission emission was was observed observed under under 316 316 nm nm excitation. excitation. As mentioned in the introduction, incident photons tend to deposit all the energy on the photoelectrons generated by interacting with CdTe, a nanomaterial of high atomic number, through the photoelectric effect. This energy goes through an energy cascade process, where the plastic matrix and dye are excited to generate excitons. Energy transfer characteristics are maximized through fluorescent dyes. Typically, through the FRET pro-cess, energy is transferred between molecules. As the nanomaterials were loaded, the emission wavelength shifted through the FRET process and the emission intensity increased. This means that compared to conventional fluorescent dyes, quantum efficiency is increased due to nanomaterials, and thus greater fluorescence is generated. Appl.Appl. Sci. Sci. 20212021, 11, 11, x, 5210FOR PEER REVIEW 7 of7 of15 15
FigureFigure 6. 6. (a()a A) A functional functional plastic plastic scin scintillatortillator including including CdTe. CdTe. (b ()b UV-Vis) UV-Vis absorbance. absorbance. (c ()c Photolumi-) Photolumi- nescencenescence emission emission spectrum, spectrum, excitation excitation at at 316 316 nm. nm.
AsTo mentioned compare the in performancethe introduction, of a plastic incident scintillator photons produced tend to deposit by adding all the CdTe energy material on thewith photoelectrons a commercial generated scintillator, by a measurementinteracting with test CdTe, was performed a nanomaterial by placing of high a source atomic at a number,distance through of 20 mm the from photoelectric the scintillator effect. surface. This energy Considering goes thethrough half-life, an energy the radioactivity cascade process,of the Cs-137 where source the plastic is 342.28 matrix kBq. and Unlike dye are inorganic excited scintillators,to generate excitons. plastic scintillators Energy transfer rarely characteristicsgenerate photoelectric are maximized effects, through and Compton fluorescent scattering dyes. Typically, mainly occurs.through Comptonthe FRET pro- edge cess,energies energy of Cs-137is transferred used in between this experiment molecule ares. As 477.3 the keV. nanomaterials Since the plastic were scintillatorloaded, the is emissiondominated wavelength by Compton shifted scattering, through energy the FR calibrationET process was and performed the emission using intensity the Compton in- creased.edge and This measurement means that testscompared were performedto conventional for 10 fluorescent min. The results dyes, quantum of the measurement efficiency istest increased using a due point to source nanomaterials, for each plastic and th scintillatorus greater arefluorescence shown in Figureis generated.6. Additionally, the resultTo ofcompare calculating the performance the output by of gross a plastic count sc ofintillator the measured produced spectrum by adding is shown CdTe in ma- the terialTable with2. The a relativecommercial efficiency scintillator, of the CdTe-loaded a measurement plastic test scintillator was performed was calculated by placing using a sourceEquation at a (2)distance as the grossof 20 mm counting from methodthe scinti forllator the commercialsurface. Considering plastic scintillator, the half-life, and the asa result, it was confirmed that it increased by 25% compared to the commercial plastic scintil- radioactivity of the Cs-137 source is 342.28 kBq. Unlike inorganic scintillators, plastic scin- lator. However, the measurement result using the point source analyzed that the Compton tillators rarely generate photoelectric effects, and Compton scattering mainly occurs. edge of commercial plastics has better resolution. This is because of the transmission loss Compton edge energies of Cs-137 used in this experiment are 477.3 keV. Since the plastic due to Rayleigh scattering, and aggregation of a solid form CdTe nanomaterials. scintillator is dominated by Compton scattering, energy calibration was performed using the Compton edge and measurement tests were performed for 10 min. The results of the Table 2. Compared relative efficiency for detection of radioactive cesium. measurement test using a point source for each plastic scintillator are shown in Figure 6. Additionally, the result of calculating the output by gross countRelative of the measuredDetection spectrum Net Count is shown in the Table 2. The relative efficiency of the CdTe-loadedEfficiency plastic scintillatorEfficiency was (cps) calculated using Equation (2) as the gross counting method for(%) the commercial(%) plastic scintillator, and as a result,20 mm it was confirmed 3,644,431 ±that495,634 it increased 100.00by 25% compared 2.09 to the Commercial 50 mm 1,332,009 ± 99,208 100.00 0.76 commercialplastic plastic scintillator. However, the measurement result using the point source analyzed that the Compton100 mm edge of commercial 474,203 ± 23,352plastics has better 100.00 resolution. This 0.27 is be- cause of the transmission20 mmloss due to Rayleigh 1,803,557 scattering,± 2657 and aggregation 49.49 of a solid 1.03 form Plastic without 50 mm 781,528 ± 582 58.67 0.45 CdTe nanomaterials.CdTe In addition, the detection100 mm efficiency of 303,323 commercial± 53 plastics and 63.96 the CdTe plastic 0.17 scin- tillator was measured. The20 mm detection efficiency 4,100,748 ±was558,312 calculated using 112.52 Equation (3). 2.35 In Table Plastic with 2, the gross count rate 50increased mm as the 1,608,902 CdTe ±nanomaterial120,952 was 120.79 added. This means 0.92 that CdTe ± the high atomic number100 of mmCdTe increases 593,654 the reaction331 rate with 125.19photons, thereby 0.34 improv- ing the efficiency. Appl. Sci. 2021, 11, x FOR PEER REVIEW 8 of 15