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A passive REM counter based on CR39 SSNTD coupled with a boron converter Agosteo, S. 1 Caresana, M. 1 Ferrarini. M 1 Silari.M 2 1)Politecnico di Milano,

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Presentation on theme: "A passive REM counter based on CR39 SSNTD coupled with a boron converter Agosteo, S. 1 Caresana, M. 1 Ferrarini. M 1 Silari.M 2 1)Politecnico di Milano,"— Presentation transcript:

1 A passive REM counter based on CR39 SSNTD coupled with a boron converter Agosteo, S. 1 Caresana, M. 1 Ferrarini. M 1 Silari.M 2 1)Politecnico di Milano, Dipartimento di Energia, Piazza Leonardo da Vinci, 32, Milano, Italy 2)CERN, 1211 Geneva, 23 CH 24th ICNTS-Bologna 2008

2 REM counters are neutron dosemeters made of a thermal neutron detector surrounded by a shell of moderating materials, such as polythene, with metal insets. They are designed to have a spectral response that is proportional to the fluence to ambient dose equivalent H*(10) conversion coefficients. The counts of the thermal neutron detector are proportional to H*(10) REM counters designed for high energy applications usually have heavy metal insets (Lead, Tugnsten) to extend their response to high energy neutrons up to 1 -2 GeV.

3 A CR39 SSNTD coupled with a Boron converter was used as thermal neutron detector. The detector exploits the (n,α)reactions on the 10 B inside the boron converter. Both α particles and 7 Li ions are produced in the reaction, and they are detected by the CR39 SSNTD.

4 α particles with energies up to 1.47 MeV are produced. Their range in the material is in the order of 7 μm. This makes etching a very delicate procedure. α particles with energies up to 1.47 MeV are produced. Their range in the material is in the order of 7 μm. This makes etching a very delicate procedure. The etching time has been chosen as a compromise between track radius and contrast. The etching time has been chosen as a compromise between track radius and contrast. The etching is made with NaOH 25% solution, 98°C, 40 minutes The etching is made with NaOH 25% solution, 98°C, 40 minutes

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8 Tracks are almost perfectly round and they have similar parameters (such as greyscale, sharpness) It is so possible to plot the parameters and to distinguish between tracks coming from thermal neutrons (via the n,α reaction on 10 B) and others coming from other sources, such as NORM, dust

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11 With this noise reduction methods, a background track density of 3±3 tracks/cm 2 has been achieved. The sensitivity to thermal neutrons have been measured in 6E-3 tracks/n

12 A passive REM counter designed to host at its centre a CR39+BE10 detector has been designed. The detector has been calibrated at Politecnico di Milano, with a Pu-Be source. Using an enriched boron converter its sensitivity is 7 tracks/cm 2  Sv. The background, due to the background reduction algorythm used, is 3 ±3 tracks/cm2. This implies a LDL of 2  Sv.

13 The detector has been tested in high energy fields both at GSI Cave A and at CERF At GSI high energy neutrons are generated by 400 MeV/u C ions impinging on a carbon target. At GSI high energy neutrons are generated by 400 MeV/u C ions impinging on a carbon target. Measurements have been made inside the ernty maze and out of the cave shielding, with dose rates ranging between 2-40  Sv/h. Measurements have been made inside the ernty maze and out of the cave shielding, with dose rates ranging between 2-40  Sv/h.

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15 The measurements have been carried out in the frame of the CONRAD project, involving several european laboratories. The measurements have been carried out in the frame of the CONRAD project, involving several european laboratories. The measurement in OC13 has been made with an integral dose of 12 μSv, and is still expoloitable. And has a statistical significance.

16 Measurements at CERF CERN-EU reference field The high energy neutrons are obtained by 150 Gev protons impinging on metal targets (Cu- Al).

17 Several measurements have been made, intercomparing with different instruments. (PoliMi-CERN) An intercomparison was made between the passive REM counter, the CERN acive Linus, and two commercial units (Thermo-electron Wendi, and Berthold)

18 The measurements show a good agreement between the passive REM counter and other extended range REM counters (such as the CERN Active Linus)

19 The detector has a high uncertainty (if compared to active REM counters), because of Poisson uncertainty: 7 tracks/cm 2 μSv mean that a 10 μSv measurement is made with 70±8 tracks, that means a 12% uncertainty. This is unavoidable Poisson uncertainty: 7 tracks/cm 2 μSv mean that a 10 μSv measurement is made with 70±8 tracks, that means a 12% uncertainty. This is unavoidable Lot uncertainty: the tracks are formed at the very surface of the detector. Different lot of detectors may have slightly different properties in the first microns from the surface, that can cause a systematic shift of the mesurements (up to 20%). This can be avoided calibrating every lot of CR39. Lot uncertainty: the tracks are formed at the very surface of the detector. Different lot of detectors may have slightly different properties in the first microns from the surface, that can cause a systematic shift of the mesurements (up to 20%). This can be avoided calibrating every lot of CR39.

20 The Boron converter may be contaminated (~0.1 mBq/cm 2 ) with NORM. This can cause problems in long term measurements. This problem can be solved because the tracks can be distinguished in the greyscale to radius plot.

21 The method is very sensitive, and it can provide reliable measurements even with integral doses down to 10 μSv. The LDL is in the order of 2 μSv. The method is very sensitive, and it can provide reliable measurements even with integral doses down to 10 μSv. The LDL is in the order of 2 μSv. It has an uncertainty significantly higher than active REM counters due to poisson uncertainty. It has an uncertainty significantly higher than active REM counters due to poisson uncertainty. It is especially suitable for routine area environmental monitoring where a large number of measurements point are needed (es. large plants), or where a large active environmental neutron monitoring system is not justified (es. conventianal radiotherapy centres) It is especially suitable for routine area environmental monitoring where a large number of measurements point are needed (es. large plants), or where a large active environmental neutron monitoring system is not justified (es. conventianal radiotherapy centres)


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