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BAS-ION Istituto di Radioprotezione
A new CR-39 nuclear track passive thoron measuring device
Massimo Calamosca, Silvia Penzo
24th International Conference on
Nuclear Tracks in Solids Bologna
1-5 September 2008
224th International Conference on Nuclear Tracks in Solids
ThoronThoron scenarioscenario
Insufficient knowledge compared to radonInsufficient knowledge compared to radon
Not explicitly addressed from the national lawNot explicitly addressed from the national law
No standard measurement method availableNo standard measurement method available
Scarcity of available calibration facilities Scarcity of available calibration facilities
Absence of intercomparisons up to nowAbsence of intercomparisons up to now
Usually the thoron risk caused by TnDP is not evaluatedUsually the thoron risk caused by TnDP is not evaluated
Short TShort T1/21/2
Low exhalation probabilityLow exhalation probability
In-homogeneity of thoron concentration In-homogeneity of thoron concentration
324th International Conference on Nuclear Tracks in Solids
Interest in risk assessment of thoron exposure is Interest in risk assessment of thoron exposure is world-wide increasingworld-wide increasing
ThoronThoron scenarioscenario
Specific thoron harm >specific radon harm for the same CSpecific thoron harm >specific radon harm for the same Ceqeq
CCpp thoron (75.66 nJ Bq thoron (75.66 nJ Bq-1-1) > C) > Cpp radon (5.56 nJ Bq radon (5.56 nJ Bq-1-1))
Some building materials (as for instance in the case of tuff) Some building materials (as for instance in the case of tuff) can cause can cause 220220Rn decay products exposure comparable or also Rn decay products exposure comparable or also greater to greater to 222222Rn decay products exposureRn decay products exposure
424th International Conference on Nuclear Tracks in Solids
The standard procedure proposed by ENEA to The standard procedure proposed by ENEA to assess equivalent dose due to thoron exposure assess equivalent dose due to thoron exposure
Sampling selection.Sampling selection.
Mean thoron gas concentration measurement by ATD-PD.Mean thoron gas concentration measurement by ATD-PD.
Experimental determination of effective room diffusion Experimental determination of effective room diffusion coefficient.coefficient.
Thoron exhalation rate from room surfaces.Thoron exhalation rate from room surfaces.
Thoron decay products (TnDP) concentration computationThoron decay products (TnDP) concentration computation
Experimental validation of the computed TnPD mean Experimental validation of the computed TnPD mean concentrations.concentrations.
Definition of occupancy factor and exposure assessment.Definition of occupancy factor and exposure assessment.
DE assessment by applying the conversion dose factor DE assessment by applying the conversion dose factor
0,50 mSv (mJ h m0,50 mSv (mJ h m33))-1-1..
524th International Conference on Nuclear Tracks in Solids
The new ENEA ATD-TnPD The new ENEA ATD-TnPD
Closed type, under patent, to be used coupled to our ATD-RnPDClosed type, under patent, to be used coupled to our ATD-RnPD
Start pointStart point: ATD-RnPD (patent : ATD-RnPD (patent MI2006A000703) with changes MI2006A000703) with changes aimed to aimed to
Increase of the diffusion Increase of the diffusion free surfacefree surface
Reduction of the Reduction of the diffusion timediffusion time
Increase of thoron Increase of thoron concentration concentration
Increase the thickness of Increase the thickness of the window between the the window between the volume of the device and volume of the device and the ATD surfacethe ATD surface
Improve the thoron sensitivity:Improve the thoron sensitivity:
Decrease the radon sensitivity:Decrease the radon sensitivity:
624th International Conference on Nuclear Tracks in Solids
Diffusion kinetic test facilitiy: schematic diagramDiffusion kinetic test facilitiy: schematic diagram
Pump
Radon Chamber
Radonsource
8,8 MeV
8,8 MeV
6,8 MeV
6,8 MeV
ATD-TnPD
ATD-RnPD
Filter
MCA
Preamplifiers
Test Chamber
Amplifiers
Preamplifier
PC
Biassupply
Filter
N2 tank
Flowmeter
Exit tothe fumehood
The CR-39 detectors in the ATD-RnPD and ATD-TnPD have been The CR-39 detectors in the ATD-RnPD and ATD-TnPD have been substituted by PIPS detectors to record the time development of the substituted by PIPS detectors to record the time development of the spectra due to the radon exposure of the two ATD-PD spectra due to the radon exposure of the two ATD-PD
Flow rate=1300 l/h
724th International Conference on Nuclear Tracks in Solids
Diffusion kinetic test Diffusion kinetic test
Requirements to perform the testRequirements to perform the test High radon concentration (High radon concentration (~~ 400 kBq/m400 kBq/m33) ) Concentration in the radon chamber ≥ 90% equilibrium valueConcentration in the radon chamber ≥ 90% equilibrium value
The equilibrium in the test chamber is reached very fast: tThe equilibrium in the test chamber is reached very fast: t90%90%=19 s =19 s
=> the delay time does not affect significantly the measurement => the delay time does not affect significantly the measurement uncertaintyuncertainty
Dwelling time = 600 sDwelling time = 600 s
The alpha energy spectra, sequentially saved with short dwelling The alpha energy spectra, sequentially saved with short dwelling times, were analysed and corrected for the times, were analysed and corrected for the 218218Po and Po and 214214Po spectra Po spectra spill overspill over the the 222222Rn ROIRn ROI
Asymptotic Asymptotic concentration concentration growth in the growth in the
radon chamberradon chamber
824th International Conference on Nuclear Tracks in Solids
Diffusion kinetic test: resultsDiffusion kinetic test: results
Increase of Increase of radon radon
concentration concentration in the two in the two devicesdevices
3.08 min (2.323.08 min (2.32÷÷4.58) (k=2) ATD-TnPD4.58) (k=2) ATD-TnPD
20.8 min (15.320.8 min (15.3÷÷32.4) (k=2) ATD-RnPD32.4) (k=2) ATD-RnPDMean diffusion timeMean diffusion time
6.0 % (4.06.0 % (4.0÷÷8.0) (k=2) ATD-RnPD8.0) (k=2) ATD-RnPD
30.3 % (22.630.3 % (22.6÷÷36.6) (k=2) ATD-TnPD36.6) (k=2) ATD-TnPD
Equilibrium ratio between Equilibrium ratio between internal and external internal and external 220220Rn Rn concentrationconcentration
0,00
0,10
0,20
0,30
0,40
0,50
0,60
0,70
0,80
0,90
0 500 1000 1500 2000 2500 3000 3500
Co
un
ting
ra
te R
n-2
22
[cp
s]
Time [s]
ATD-RnDP
ATD-TnDPy=0.768*(1-Exp(-8.0E-4*x))
R2 = 0.87
y=0.669*(1-Exp(-5.42E-3*x))
R2 = 0.73
924th International Conference on Nuclear Tracks in Solids
Thoron exposure: the calibration exposure chamberThoron exposure: the calibration exposure chamber
Thoron Chamber
MCA
Preamplifier
PC
Biassupply
Filter
Filter
Flowmeter
Pump
Thoronsource
2° Filter
1° Filter
Amplifier
Si Detector
Pressuremeter
By pass
Pressuremeter
Temperaturemeter
Cleaning air
Filter
Exit to fume hood Fan
Flow rate = 18.0 l/min
1024th International Conference on Nuclear Tracks in Solids
Thoron exposure: the Thoron exposure: the 220220Rn sourceRn source
Sample ofSample of Monazite Monazite mineralmineral was crushed, sieved and wet-grinded by was crushed, sieved and wet-grinded by a Turbula to reduce the grain size to a Turbula to reduce the grain size to ~~ 1µm, so to increase the thoron 1µm, so to increase the thoron emanation. emanation. The suspension obtained was filtered and piled up in set of 15 filters.The suspension obtained was filtered and piled up in set of 15 filters.The sourceThe source is constituted by 3 towers of 15 filters each, 3 mm is constituted by 3 towers of 15 filters each, 3 mm spaced, connected in series and installed within a stainless-steel spaced, connected in series and installed within a stainless-steel vessel.vessel.
232232Th and Th and 226226Ra activities measured by HPGeRa activities measured by HPGe232232Th=(8.82±0.19) kBq, Th=(8.82±0.19) kBq, 226226Ra (355±18) Bq, Ra (355±18) Bq, 226226Ra/Ra/232232Th = 4%Th = 4%
1124th International Conference on Nuclear Tracks in Solids
How to determine the thoron exposure:How to determine the thoron exposure: the thoron monitor (TM) the thoron monitor (TM)
A new monitor based on the two-filter method has been devised to A new monitor based on the two-filter method has been devised to absolutely measure the absolutely measure the 220220Rn concentration Rn concentration directlydirectly at the exit of the at the exit of the chamber. chamber.
It consists of a small aluminium cylindrical tube with two filters in It consists of a small aluminium cylindrical tube with two filters in series separated by a delay volume to permit series separated by a delay volume to permit 220220Rn decay, Rn decay, 216216Po Po growth and a negligible presence of growth and a negligible presence of 218218Po.Po.
1224th International Conference on Nuclear Tracks in Solids
The thoron monitor: sectorsThe thoron monitor: sectors
1° sector 1° sector (sampling head & (sampling head &
1° filter)1° filter)
2° sector 2° sector (Body)(Body)
3&4° sectors 3&4° sectors (PIPS)(PIPS)
5° sector 5° sector (Volume & 2° (Volume & 2°
filter)filter)
1324th International Conference on Nuclear Tracks in Solids
Thoron exposure: the thoron monitorThoron exposure: the thoron monitor
The thoron concentration is determinated by The thoron concentration is determinated by 220220Rn and Rn and 216216Po Po counts counts counted during the sampling (1000 s). counted during the sampling (1000 s).
0
0,2
0,4
0,6
0,8
1
0 0,1 0,2 0,3 0,4 0,5 0,6 0,7
Act
ivity
to in
let R
n-2
20
co
nce
ntr
atio
ns
ratio
Transit time [s]
Rn-220
Po-216 -1° stage
Po-216 -2° stage
Po-216 - PIPS
Po-216 -4° stage
Po-216 -5° stage1° filter
2° filter
1424th International Conference on Nuclear Tracks in Solids
Thoron monitor: uncertainty budgetThoron monitor: uncertainty budget
Uncertainty sources on instrument response ∂f/∂x u(x) (∂f/∂x)2*u2(x) Weight Loss constant sector 2 1,4E+01 1,2E-01 2,9E+00 41,1% Filter efficiency (216Po) 9,7E+02 1,4E-03 1,9E+00 26,7%
216Po 1,1E+01 6,6E-02 5,3E-01 7,50% Loss constant sector 4 2,0E+00 3,6E-01 5,1E-01 7,14% Loss constant sector 5 5,3E-01 1,3E+00 4,4E-01 6,13%
Flow 1,9E-01 3,0E+00 3,2E-01 4,56% Loss constant sector 3 6,1E-01 7,7E-01 2,2E-01 3,11%
Diameter sector 4 2,9E+00 1,1E-01 9,8E-02 1,37% Height sector 4 7,6E+00 4,0E-02 9,2E-02 1,30% Height sector 5 1,1E+00 1,7E-01 3,8E-02 0,53%
counting volume efficiency sector 4 2,5E+02 4,3E-04 1,2E-02 0,17% Diameter sector 2 7,8E-01 1,1E-01 6,8E-03 0,10% Diameter sector 5 8,6E-01 8,8E-02 5,7E-03 0,08%
counting volume efficiency sector 5 7,5E+01 9,7E-04 5,3E-03 0,074% Diameter & height sector 4 (Covariance) 9,0E-01 - 3,8E-03 0,054% counting surface efficiency sector 5 1,8E+01 2,2E-03 1,6E-03 0,022%
Diameter sector 3 3,3E-01 1,1E-01 1,2E-03 0,017% Height sector 2 7,5E-02 4,6E-01 1,2E-03 0,017%
Sum - - 7,1 -
1524th International Conference on Nuclear Tracks in Solids
Thoron exposure: calibration resultsThoron exposure: calibration results
Low Exposure Medium Exposure High Exposure
Exposure time [s] 83886 60360 233487
Post exposure time [s] 252000 252000 252000
Mean circuit flow [cm3 s-1] 315.5 306.5 302.8
N. Sampling 5 4 3
Mean counts±SD 85.6±4.1 252±19 249.3±6.3
Mean u(counts)±SD 9.25±0.22 15.85±0.61 15.78±0.20
Mean TnMR ±SD [Bq m-3] 129.62±0.83 132.7±1.2 131.64±0.37
Mean u(TnMR)±SD [Bq m-3] 2.592±0.017 2.654±0.024 2.6328±0.0073
Mean TnM concentration±SD [kBq m-3] 11.10±0.58 33.4±2.8 32.82±0.92
Mean u( TnM concentration)±SD [kBq m-3] 1.219±0.036 2.21±0.11 2.179±0.036
Mean TnM flow±SD [cm3 s-1] 311.1±4.4 295.0±6.0 300.4±1.9
Mean volume post chamber correction ±SD 1.001243±0.000018 1.001311±0.000027 1.0012872±0.0000080
Mean chamber transit time ±SD [s] 51.04±0.73 53.8±1.1 52.85±0.83
Mean transit time correction±SD 1.3980±0.0070 1.425±0.011 1.4155±0.0032
Mean chamber concentration±SD [kBq m-3] 15.82±0.88 47.7±4.2 46.4±1.4
Mean u(chamber concentration)±SD [kBq m-3] 1.707±0.058 3.16±0.18 3.096±0.059
Sampling vs. circuit flow correction 0.9970 0.9827 0.9983
Exposure [kBq h m-3] 360 1090 3008
u(Exposure) [kBq h m-3] 44 110 220
1624th International Conference on Nuclear Tracks in Solids
Thoron exposure: calibration test designThoron exposure: calibration test design
3 thoron exposures3 thoron exposures
(360 ± 44) kBq h m(360 ± 44) kBq h m-3-3
(109 ± 11) (109 ± 11) 10 kBq h m10 kBq h m-3-3
(301 ± 22) (301 ± 22) 10 kBq h m10 kBq h m-3-3
3 radon exposures3 radon exposures
(273 ± 11) kBq h m(273 ± 11) kBq h m-3-3
(1365 ± 53) kBq h m(1365 ± 53) kBq h m-3-3
(395 ± 15) (395 ± 15) 10 kBq h m10 kBq h m-3-3
12 ATD-TnPDs12 ATD-TnPDs
6 ATD-RnPDs6 ATD-RnPDs
6 ATD-RnPDs (off position)6 ATD-RnPDs (off position)
6 ATD-TnPDs6 ATD-TnPDs
6 ATD-RnPDs6 ATD-RnPDs
Reference radon exposureReference radon exposure
(260 ± 10) (260 ± 10) 10 kBq h m10 kBq h m-3-36 ATD-RnPDs6 ATD-RnPDs
114 ATD-PDs114 ATD-PDs7 different etching times7 different etching times
Removed Layer range :Removed Layer range :
(7.84 ± 0.04) ÷ (12.54 ± 0.05 ) µm (7.84 ± 0.04) ÷ (12.54 ± 0.05 ) µm
1724th International Conference on Nuclear Tracks in Solids
The thoron chamber exposure: procedure requirementsThe thoron chamber exposure: procedure requirements
A high (18 lpm) circulating flow must be hold for all the course of A high (18 lpm) circulating flow must be hold for all the course of exposure exposure
To minimize To minimize 220220Rn decay the volume of the tubing Rn decay the volume of the tubing has to be kept as the minimumhas to be kept as the minimum
To minimize in-homogeneity exposure within the chamber, To minimize in-homogeneity exposure within the chamber, the use of a fan to mix air has been adoptedthe use of a fan to mix air has been adopted
To prevent the growing of radon in the circuitTo prevent the growing of radon in the circuitNitrogen has to be fluxed through the chamber at least every 24 hNitrogen has to be fluxed through the chamber at least every 24 h
The ATD-PD were stored for at least 70 h in a radon proof container The ATD-PD were stored for at least 70 h in a radon proof container to get the irradiation equilibrium for to get the irradiation equilibrium for 212212Bi (Bi (212212Pb)Pb)
1824th International Conference on Nuclear Tracks in Solids
Thoron exposure: net track density evaluationThoron exposure: net track density evaluation
D(TnPD,Tn Rn) ETn SENS(Tn,TnPD) ERn SENS(Rn,TnPD)
D(RnPD,Tn Rn) ETn SENS(Tn,RnPD) ERn SENS(Rn ,RnPD)
SENS(TnPD,Rn)
SENS(RnPD,Rn)
SENS(RnPD,Tn)
SENS(TnPD,Tn)
D(TnPD,Tn) D(TnPD,Tn Rn) D(RnPD,Tn Rn)
1
SENS(TnPD,Tn) D(TnPD,Tn)
ETn
Where D(XPD,Tn+Rn) is the track density measured in the X Where D(XPD,Tn+Rn) is the track density measured in the X passive device exposed to mixed irradiation (Tn+Rn, or Tn or Rn)passive device exposed to mixed irradiation (Tn+Rn, or Tn or Rn)
Where SENS(X,Y) is the response or sensitivity of the X passive Where SENS(X,Y) is the response or sensitivity of the X passive device to the Y (Tn or Rn) gasdevice to the Y (Tn or Rn) gas
1924th International Conference on Nuclear Tracks in Solids
Thoron exposure results: Thoron exposure results: dependence on etching time dependence on etching time
0,02
0,04
0,06
0,08
0,1
0,12
0,14
8 9 10 11 12 13 14 15 16 17
Diameter D95%
= 0. 056+0.00300D95%
R2 = 0.67, P<0.05, N=7
SENS(RnPD,Tn)
SENS(TnPD,Tn)
2024th International Conference on Nuclear Tracks in Solids
0,5
0,55
0,6
0,65
0,7
0,75
0,8
0,85
0,9
8 9 10 11 12 13 14 15 16 17
Diameter D95%
= 0.940 - 0.0218D95%
R2 = 0.912, P<0.01, N=7
Thoron exposure results: Thoron exposure results: dependence on etching time dependence on etching time
SENS(TnPD,Rn)
SENS(RnPD,Rn)
2124th International Conference on Nuclear Tracks in Solids
1
1,5
2
2,5
3
3,5
4
4,5
5
8 9 10 11 12 13 14 15 16 17 18
SE
NS
[(T
rack
s cm
^-2)
/(kB
q h
m^-
3)]
Diameter D95% [pixel]
SENS (ATD-TnPD,Rn)
SENS (ATD-RnPD,Rn)
Thoron exposure results: response of both Thoron exposure results: response of both devices to radon vs. etching timedevices to radon vs. etching time
2224th International Conference on Nuclear Tracks in Solids
0
0,05
0,1
0,15
0,2
0,25
0,3
8 9 10 11 12 13 14 15 16 17 18
SE
NS
[(T
rack
s cm
^-2
)/(k
Bq
h m
^-3
)]
Diameter D95% [pixel]
SENS(ATD-RnPD,Tn)
y=0.214*(1-Exp(-0.1903*(x-4,91)))R2 = 0.78
Thoron exposure results: response of radon Thoron exposure results: response of radon passive device to toron vs. etching timepassive device to toron vs. etching time
2324th International Conference on Nuclear Tracks in Solids
1,2
1,3
1,4
1,5
1,6
1,7
1,8
1,9
8 9 10 11 12 13 14 15 16 17 18
SE
NS
[(Tr
acks
cm
^-2)
/(kB
q h
m^-
3)]
Diameter D95% [pixel]
SENS = 1.840(1-Exp(-0.1826D95%))R2 = 0.941, P<0.01, N=7
Thoron exposure results: response of toron Thoron exposure results: response of toron passive device to toron vs. etching timepassive device to toron vs. etching time
2424th International Conference on Nuclear Tracks in Solids
ConclusionConclusion
The new ATD-TnPD has been completely characterised.The new ATD-TnPD has been completely characterised. The responses (SENS) to toron and radon result a little better than The responses (SENS) to toron and radon result a little better than
our previsions based on the preliminary testsour previsions based on the preliminary testsWe are always looking for an external calibration We are always looking for an external calibration
The new thoron source and monitor have resulted very effective, so The new thoron source and monitor have resulted very effective, so to be considered fit to be used in the calibration step.to be considered fit to be used in the calibration step.
And for the future…And for the future… A finer determination of the diffusion losses, that result the primary A finer determination of the diffusion losses, that result the primary
sources of uncertainty, is to be worked out, …sources of uncertainty, is to be worked out, …
Thank You for your attention… Thank You for your attention… and patienceand patience
2524th International Conference on Nuclear Tracks in Solids
0
5000
10000
15000
20000
25000
0 500 1000 1500 2000
Tra
ck d
en
sity
[tra
cks/
cm^2
]
220-Rn Exposure [kBq h/m^3]
ATD-RnPD
ATD-TnPD
SENS (ATD-RnPD) = 1.683±0.033
(tracks cm -2)/(kBq h m-3)
SENS (ATD-TnPD) = 9.98±0.14
(tracks cm -2)/(kBq h m-3)
Here is what did occur at PTB Here is what did occur at PTB !!