Uncertainty in radon measurements with CR39 detector due to unknown deposition of Po

Similar documents
Sensitivity of LR 115 detectors in hemispherical chambers for radon measurements

Theoretical basis for long-term measurements of equilibriumfactors using LR 115 detectors

RADON EQUILIBRIUM MEASUREMENT IN THE AIR *

LONG-TERM MEASUREMENTS OF RADON PROGENY CONCENTRATIONS WITH SOLID STATE NUCLEAR TRACK DETECTORS

Multilayer Nuclear Track Detectors for Retrospective Radon Dosimetry

INFLUENCE OF EXPOSURE GEOMETRY ON THE RESPONSE OF CR39 SSNT RADON DETECTORS *

Chemical etching characteristics for cellulose nitrate

Nuclear Instruments and Methods in Physics Research B 247 (2006)

Response uniformity of a large size RPC

Measurement of material uniformity using 3-D position sensitive CdZnTe gamma-ray spectrometers

Alpha-particle fluence in radiobiological experiments

SYSTEM OF MONITORING THE ATMOSPHERICAL RADON WITH AN IONIZATION CHAMBER DETECTOR TYPE IN PULSE MODE

V.Schmidt, P. Hamel. Radon in the Living Environment, April 1999, Athens, Greece

Performance Characterization of A New Cam System M.J. Koskelo 1, J.C. Rodgers 2, D.C. Nelson 2, A.R. McFarland 3 and C.A. Ortiz 3

Long-term measurements ofradon progeny concentrations with solid-state nuclear track detectors

Influence of aerosol concentration and multivariate processing on the indication of radon progeny concentration in air

Physics sources of noise in ring imaging Cherenkov detectors

CALIBRATION OF INSTRUMENTS MEASURING RADON OVER A LARGE ACTIVITY RANGE. N. Michielsen, V. Voisin

Measurement of Radon and Uranium Concentrations and Background Gamma Rays at the University of Baghdad -Jadiriyah Site

Light weight concrete: 226 Ra, 232 Th, 40 K contents and dose reduction assessment

Modeling radon daughter deposition rates for low background detectors

Measurement of radon ( 222 Rn) and thoron ( 220 Rn) concentration with a single scintillation cell

A pattern recognition method for the RICH-based HMPID detector in ALICE

2) Explain why the U-238 disintegration series shown in the graph ends with the nuclide Pb-206.

Formation and growth of tracks in nuclear track materials

Since the beam from the JNC linac is a very high current, low energy beam, energy loss induced in the material irradiated by the beam becomes very lar

Alpha-Energies of different sources with Multi Channel Analyzer

arxiv:hep-ex/ v1 5 Apr 2000

cross section limit (95% CL) N = B = 10 N = B = 3 N = B = 0 number of experiments

A. Aleksanyan, S. Amirkhanyan, H. Gulkanyan*, T. Kotanjyan, L. Poghosyan, V. Pogosov

Stopping power for MeV 12 C ions in solids

RADIOACTIVITY IN THE AIR

Reconstruction algorithms in the Super-Kamiokande large water Cherenkov detector

Gaussian process for nonstationary time series prediction

Count. Count. 200mm. PMT scintillation. PMT flourescence. PMT fluorescence. PMT fluorescence. PMT fluorescence. 50mm. 42mm

Radioactivity. (b) Fig shows two samples of the same radioactive substance. The substance emits β-particles. Fig. 12.1

Air Filter Alpha Spectrometry Report

One-dimensional thermoluminescence kinetics

Analysis of gross alpha, gross beta activities and beryllium-7 concentrations in surface air: their variation and statistical prediction model

arxiv:nucl-ex/ v2 21 Jul 2005

A Simple Measurement Technique of the Equilibrium. Equivalent Thoron Concentration with a CR-39 Detector

Methodology for the radiological assessment of noble gases in nonhuman

Optical bistability in metal/dielectric composite with interfacial layer

First tests of the big volume ultra low background gamma spectrometer

Ordering periodic spatial structures by non-equilibrium uctuations

Safety: Do not eat the radioactive candium until it has decayed into a safer element.

RADIOACTIVITY Q32 P1 A radioactive carbon 14 decay to Nitrogen by beta emission as below 14 x 0

ISO Water quality Measurement of polonium 210 activity concentration in water by alpha spectrometry

Pixels GaAs Detectors for Digital Radiography. M.E. Fantacci. and. Abstract

Particle Size of Radioactive Aerosols Generated During Machine Operation in High-energy Proton Accelerators

Drift plane. substrate (20ÉIm polyimide) 200ÉIm. Back strip (180ÉIm width) Base (Ceramic) Anode strip (10ÉIm width) Cathode strip (100ÉIm width)

13.2 NUCLEAR PHYSICS HW/Study Packet

A novel approach for long-term determination of indoor 222 Rn progeny equilibrium factor using nuclear track detectors

7.2 RADIOACTIVE DECAY HW/Study Packet

Theoretical model of electrostatic precipitator performance for collecting polydisperse particles

Radionuclides in hot mineral spring waters in Jordan

Measurement of indoor radon, thoron and annual effective doses in the some dwellings of Jaipur city, Rajasthan, India

Higher -o-o-o- Past Paper questions o-o-o- 3.6 Radiation

INTERNATIONAL STANDARD

ATOMIC PHYSICS Practical 11 STUDY OF DECOMPOSITION OF RADIOACTIVE RADON 1. INTRODUCTION

Analysis of Radioactive Disequilibrium in Natural Decay Chains due to Processing

Chapter 30 Nuclear Physics and Radioactivity

L 37 Modern Physics [3]

Improving neutron detection efficiency by using passive converters

Electrostatic charging e ects in fast H interactions with thin Ar

Z 14. 2, 3, 4, 7, 10, 13 Contaminated Soil (Photon source) 5, 6, 9, 11, 12 Gap 8 NaI Crystal

Determination of thorium and uranium contents in soil samples using SSNTD s passive method

Monte Carlo Simulation concerning Particle Therapy

Uranium Concentrations measurement for Ground Water and Soil Samples in Al-Najaf/Iraq

Ion Chamber. Radon Measurements. Theremino System Rev.1. Theremino System IonChamber_ENG Page 1

Determining the Efficiency of a Geiger Müller Tube

This document is a preview generated by EVS

Fuzzy relational equation with defuzzication algorithm for the largest solution

The e!ects of the concentration of a polymer dispersant on apparent viscosity and sedimentation behavior of dense slurries

RADIOACTIVITY. Nature of Radioactive Emissions

RESPONSE OF A RADON CHARCOAL CANNISTER TO CLIMATIC AND RADON VARIATIONS IN THE INTE RADON CHAMBER. A. Vargas, X. Ortega, I.

Radioactivity. The Nobel Prize in Physics 1903 for their work on radioactivity. Henri Becquerel Pierre Curie Marie Curie

y loo Physics Essentials Workbook Stage 2 Physics Exercises

Electrical conductivity of air related to ion pair production rate from radon and its progeny concentrations in dwellings of Mysore city

Experiment Radioactive Decay of 220 Rn and 232 Th Physics 2150 Experiment No. 10 University of Colorado

Second year seminar. Massimiliano Marchisone. Torino, 03/05/2013. Università di Torino e INFN Université Blaise Pascal de Clermont-Ferrand et LPC

ARMUG New CAM Developments. Arran Morgan MSc Physicist

(a) (i) State the proton number and the nucleon number of X.

ISO Measurement of radioactivity in the environment Air: radon-222 Part 5: Continuous measurement method of the activity concentration

Breakdown limit studies in high-rate gaseous detectors

Strand J. Atomic Structure. Unit 2. Radioactivity. Text

Alpha-energies of different sources with Multi Channel Analyzer (Item No.: P )

Heavy ion fusion energy program in Russia

AEPHY: Nuclear Physics Practise Test

8.) Our radiological environment

The electromagnetic calorimeter of the HERA-B experiment

Analysis of alpha-emitting isotopes in an inorganic scintillator

Fabrication of micro-optical components in polymer using proton beam micro-machining and modification

Alpha-Gamma discrimination by Pulse Shape in LaBr 3 :Ce and LaCl 3 :Ce

International Journal of PharmTech Research CODEN (USA): IJPRIF, ISSN: , ISSN(Online): Vol.9, No.9, pp , 2016

measuring radon? Notes In this lesson, we are going to talk about the units that we use to measure radon.

Organ and effective dose rate coefficients for submersion exposure in occupational settings

Michigan State University, East Lansing MI48824, USA INTRODUCTION

Results of the 2015 national indoor radon intercomparison measurements in Serbia

σ ε ω 1 /σ ω ε α=ω 2 /ω 1

Transcription:

Nuclear Instruments and Methods in Physics Research A 450 (2000) 568} 572 Uncertainty in radon measurements with CR39 detector due to unknown deposition of Po D. NikezicH, K.N. Yu* Department of Physics and Materials Science, City University of Hong Kong, Tat Chee Avenue, Kowloon Tong, Kowloon, Hong Kong Received 23 August 1999; received in revised form 4 February 2000; accepted 9 February 2000 Abstract Uncertainty in radon measurements using the CR39 solid-state nuclear track detector in chambers is introduced by the unknown fraction f of Po that deposited onto the inner chamber walls. This uncertainty was estimated for cylindrical chambers with di!erent size in the present study. It was found that the uncertainty increased with the chamber height and radius. For short chambers with a height H"2 cm the uncertainty was less than 5%, while in tall chambers with H"7 cm it could be up to 17%. The radial track density on the CR39 detector inside the di!usion chamber was also found to be dependent on the fraction f. In this work, some examples of this dependence are shown. 2000 Elsevier Science B.V. All rights reserved. PACS: 29.40; 23.60 Keywords: Natural radioactivity; Radon; CR39 detector; Detector sensitivity; Monte Carlo methods 1. Introduction For long-term passive measurements of indoor radon ( Rn) concentrations solid-state nuclear track detectors (SSNTD) are frequently used. The most commonly used SSNTD is CR39, which is based on the polymer of alil diglycol carbonate. There are two di!erent modes of its usage in radon measurements: (a) as open (bare) detector and (b) as detector in a di!usion chamber. There are di!erent problems in both modes. In case of bare detector, humidity and dust a!ect the detection of alpha particles and the detector sensitivity is dependent * Corresponding author. Tel.: #852-2788-7812; fax: #852-2788-7830. E-mail address: peter.yu@cityu.edu.hk (K.N. Yu). on the equilibrium factor between radon and its short-lived progeny. These were the reasons for the development and wide application of di!usion chambers for radon measurements. The di!usion chamber is a cup covered with a "lter paper on the top and is frequently equipped with a CR39 detector that is usually placed on the bottom of the cup. This technique is well described in the literature and used by many workers in the "eld. Radon gas di!uses through the "lter paper into the chamber while its short-lived progeny are stopped by the "lter paper. In this way, radon measurements are independent of the equilibrium factor between radon and its progeny. Radon gas atoms entering the chamber will decay in it and form progeny atoms. There is radioactive equilibrium between radon and its progeny inside the 0168-9002/00/$ - see front matter 2000 Elsevier Science B.V. All rights reserved. PII: S 0 1 6 8-9 0 0 2 ( 0 0 ) 0 0 3 0 9-0

D. Nikezic&, K.N. Yu / Nuclear Instruments and Methods in Physics Research A 450 (2000) 568}572 569 chamber. However, progeny atoms move randomly in the chamber volume and can deposit onto available inner surfaces before decay. The deposition changes the irradiation geometry of the detector, i.e., detector sensitivity is dependent on the fraction of radon progeny decaying in the air prior to deposition. The behavior of radon progeny inside the chamber (as well as the aerosol properties and air velocity inside the chamber) is unknown and it is di$cult to estimate the fraction of radon progeny decaying prior to deposition. The deposition fraction can depend on di!erent environmental conditions (e.g., volume distribution of the electrical "eld inside the chamber), which in#uence the detector sensitivity and measurement accuracy. The objective of the present work was to determine the uncertainty in radon measurements with the CR39 detector in di!usion chambers due to the unknown behavior of Po inside the chambers. The dependence of the detector sensitivity on the distance from the center of the detector was also investigated. The "rst radon progeny Po has a relatively short half-life (3.05 min) and it can partially decay before deposition. The second and third progeny in the radon decay chain, Pb and Bi, have much longer half-lives and we considered them as completely deposited. In this way, the second alphaemitting progeny in the radon chain, Po, was assumed as totally deposited. Therefore, the present work was limited to the study of the unknown behavior of Po inside the chamber. 2. Method and model The sensitivity ε of the CR39 detector was de- "ned as the number of tracks per unit surface area for an exposure to 1 Bq m of some alpha emitter in air for 1 s (i.e. track density per unit exposure). The sensitivity ε to the nuclide i in the radon chain was called the partial sensitivity. The total sensitivity ε to the radon decay chain equals the sum of partial sensitivities to all alpha-emitting nuclides in the radon decay chain expressed as the ratio between the total number of tracks to the total surface of the detector: ε "ε #f ε #(1!f )ε #ε #p N #p N (1) where ε is the sensitivity to Po from air, ε is the sensitivity to Po from the chamber wall and ε is the sensitivity to Po from the wall, f is the part of Po that decayed in the chamber volume, p the detection e$ciency (in%) for alpha-emitting progeny (i"1 for Po, and i"4 for Po) deposited on the detector itself (or the so-called plate-out) and N is the number of emitted alpha particles on the detector surface for these progeny for unit exposure. 2.1. Geometrical model The geometry of the di!usion chamber considered in this work was cylindrical. A circular CR39 detector was situated at the bottom of the chamber so that the centers of the detector and the chamber base coincided with each other and the detector radius was equal to the radius of the chamber base. For this geometry, the detector covered the whole bottom of the chamber. Radon gas atoms were assumed to remain in air completely, i.e., no deposition. While Po was partially deposited, the other radon progeny decayed completely after deposition. A uniform deposition of radon progeny on all available surfaces of the chamber was also assumed. 2.2. Calculation model Monte Carlo method was employed for the calculation of the partial sensitivities, and the total sensitivity was determined using Eq. (1). All calculations used 10 histories. In addition, the radial sensitivity distribution on the detector was also determined. Calculations were made for the CR39 detector, with a thickness of 8 μm for the removed layer. The circular detector surface was divided into circular stripes with widths of 1 mm bounded by concentric circles. In the course of calculations, the number of alpha particles detected in di!erent circular stripes was determined to deduce the radial sensitivity distribution.

570 D. Nikezic&, K.N. Yu / Nuclear Instruments and Methods in Physics Research A 450 (2000) 568}572 A previously developed program of Nikezic et al. [1] was used in these calculations. Details of the program were described earlier and will not be repeated here. 3. Results Figs. 1a, b and c show the radial distribution of the total sensitivities for di!usion chambers with radius r"2, 3 and 4, respectively. Under these considerations the tracks from plateout are neglected. The chamber height was varied from 2 to 7 cm, and the height is given as a parameter in Fig. 1. There are two groups of curves in the "gures: the solid lines correspond to the assumption of f "1 (no deposition of Po) and the dashed lines to the assumption of f "0 (total deposition of Po). In all the cases shown in Fig. 1, the detector radius r was the same as the chamber radius r, i.e., the detector covered the entire base of the chamber. Fig. 1a gives the results for the chamber with a radius r"2 cm. The total sensitivities decrease from the center to the edge of the detector. This can be explained by the fact that the center of the detector was irradiated from all points above the detector while the edge was irradiated only from one side. This phenomenon is called the edge e!ect (or wall e!ect) in radon measurements with di!usion chambers. It can be observed that the Po deposition decreased the sensitivity of CR39 detector to the radon chain by approximately 40%. Fig. 1b gives the results for the r"3 cm chamber. The total sensitivity obtained for f "1 decreased from the center towards the edge of the detector by a factor of slightly less than 2. However, the curves for f "0 were not monotonically decreasing (except the curve for a height H"2 cm). Instead, they showed weak and broad maximum values between 1 and 2 cm from the edge of the detector. Fig. 1c gives the results for the r"4 chamber. The new feature in the curves of total sensitivities for f "1 was the relatively wide plateaus extending from the center up to 2 cm from the center, where the sensitivity is rather constant (with smaller variations). The curves for f "0 had peaks (except the curve for H"2 cm) close to the edge of the detector (about 1 cm from the end), which originated from the progeny deposited onto the wall. This peak is most expressed for tall chambers with H"6 and 7 cm. Here, the possibility to study the Po deposition behavior inside di!usion chambers through the radial track density is demonstrated. 3.1. Uncertainty Uncertainty U is de"ned in the present work as ;" ε!ε ε where ε and ε are the total sensitivities calculated for f "1 and f "0, respectively, and ε " (ε #ε )/2. The uncertainty in radon measurements introduced by an unknown f has been calculated and shown in Fig. 2 as a function of the chamber height H, with the detector radius R as a parameter (for R"2, 3 and 4 cm). The tracks originated by plateout are taken into account in the consideration of the uncertainties. It can be observed that the uncertainty increases with the chamber height. For the short chamber (H"2 cm) the uncertainty is rather small (below 5%). For H"3 cm the uncertainty is between 2% and 11%. For tall chambers (H"4 to 7 cm), the uncertainty ranges from 4% up to 16%. The largest uncertainties were recorded in the chambers with H"7 cm, and range from 7% up to 16%. 4. Discussions Po atoms are formed in the unattached mode (or free mode) in di!usion chambers from the decay of Rn. The fate of these Po atoms depends on the concentration and size distribution of aerosols inside the chamber. In general, the aerosol conditions inside a chamber are not known, and there are no data in the literature related to this question. A method for determination of f is proposed based on the results presented in this study. In large-volume chambers, e.g., r"4, H"7, the (2)

D. Nikezic&, K.N. Yu / Nuclear Instruments and Methods in Physics Research A 450 (2000) 568}572 571 Fig. 1. Sensitivity distribution in di!usion chambers with di!erent dimensions: (a) detector radius r"2 cm; (b) r"3 cm and (c) r"4 cm. The numbers attached to the curves represent the height (H) of the chambers. In all cases, the detector radius was the same as the chamber radius R, i.e., the detector covered the entire base of the chamber. The fraction of Po decayed before deposition is denoted as f. Plate-out tracks were neglected in these graphs.

572 D. Nikezic&, K.N. Yu / Nuclear Instruments and Methods in Physics Research A 450 (2000) 568}572 Fig. 2. Uncertainty in radon measurements with the CR39 detector (due to the unknown deposition behavior of Po inside the chambers) as a function of the chamber height. The results were given for chamber radii of 2, 3 and 4 cm. deposited Po will lead to a peak in the radial track distribution close to the detector edge. The height of this peak is dependent on the deposition fraction of Po. 5. Conclusions 1. The radial track density distribution depends on the deposition fraction of Po. The dependence is more prominent in larger chambers, i.e., larger chambers are more suitable to be deployed to study the deposition of Po inside di!usion chambers. 2. The size of the CR39 detector in the di!usion chamber is also important in radon measurements because the radial track density distribution and the detector sensitivity are also variable for di!erent detector sizes. 3. The unknown deposition fraction of Po introduces uncertainties in radon measurements using CR39 in di!usion chambers. The uncertainty depends on the dimensions of the chamber and detector, and the general trend is to increase with the chamber height. In large chambers, the uncertainty can be as high as 17%. References [1] D. NikezicH, C. Baixeras, D. KosticH, Nucl. Instr. and Meth. A 373 (1996) 290.