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1
Activation problems
S.Agosteo(1), M.Magistris(1,2), Th.Otto(2), M.Silari(2)
(1) Politecnico di Milano;
(2) CERN
2
Introduction
Problems of material activation:• in the target system and its surroundings (for
Neutrino Superbeam and BetaBeams)• in the machines for ion acceleration and in the
decay ring (for BetaBeams only)
An estimation of the production of residual nuclei in the target station has been performed with FLUKA
3
FLUKA simulations
• A compromise between CPU time and precision:
A simplified geometryDEFAULTS SHIELDIN, conceived for
calculations for proton accelerators
The new evaporation module is activated (EVAPORAT)
The pure EM cascade has been disabled
4
MicroShield
• A program which analyzes shielding and estimates exposure from gamma radiation
• Input:DimensionsMaterial information and build-up factorsSource strengthIntegration parameters
5
The target station
The facility consists of a target, two horns and a decay tunnel. It is shielded by 50 cm thick walls of concrete and is embedded in the rock.
Top view
6
Target and horns
A 2.2 GeV, 4 MW is sent onto the mercury target, inserted in two concentric magnetic horns for pion collection and focusing.
Proton beam
7
Decay tunnel
The decay tunnel consists of a steel pipe filled with He (1 atm), embedded in a 50 cm thick layer of concrete
60 m long
Inner diameter of 2 m
Thickness of 16 mm
Cooling system (6 water pipes)
Front view
8
Surroundings
The whole structure (target, horn and decay tunnel) is embedded in the rock, which has been divided into 100 regions for scoring the inelastic interaction distribution
9
Activation of mercury
Assumptions: 0.5 m3 of liquid circulating in the systemthe mercury is uniformly irradiatedit will circulate in pipes (2 cm radius) and
be stored in a spherical tank10 years of operation and 1 month cooling
10
Dose rates due to the mercury
Dose equivalent rate at:• 50 cm from a 1 m long pipe, filled with Hg:
320 mSv h-1
• 5 m from the tank, without shielding:
68 mSv h-1
• 10 cm from a droplet (1 mg Hg):
1 Sv h-1
11
Horn
• Material: ANTICORODAL 110 alloy (Al 96.1%)
• Irradiation time: six weeks
• Specific activity (MBq/g) at different cooling times
12
Horn, after 6 weeks of irradiation
1E-3 0.01 0.1 1 10 100 10001E-5
1E-4
1E-3
0.01
0.1
1
10
100
1000
10000
1000 years
2 years
100 years
50 years
10 years
30 days
1 day
inner part of the horn outer part of the horn
Sp
efic
ic a
ctiv
ity
(MB
q g
-1)
time of cooling (years)
13
Dose rates due to the horn
• At one metre from the horn, after six weeks of irradiation and one day of decay:
Dose equivalent rate: ~10 Sv h-1
• Equipment for the remote handling of the magnetic horns will be mandatory.
14
Steel pipe
• Material: steel P355NH (Fe 96.78%)
• 60 m long• Filled with Helium• 10 years of operation• Operational year of 6
months (1.57*107 s/y)
Steel pipe
16
Steel pipe, after 10 years of operation
1 year of cooling
0 10 20 30 40 50 60
10
100
29 MBq g-1
Sp
ecif
ic a
ctiv
ity
(MB
q/g
)
decay tunnel [m]
average value
17
Dose rates in the decay tunnel
• 89% of the dose rate comes from the steel
• The dose rate does not depend on the radial position
After ten years of operation, one month of cooling
18
Earth, after 10 years of operation
1E-3 0.01 0.1 1 10 100 10001E-3
0.01
0.1
1
10
100
1000
10000
100000
1000000
depth
10 m from the target
Sp
ecif
ic a
ctiv
ity
(Bq
/g)
years of cooling
0-1 m 1-2 m 2-3 m 3-4 m 4-5 m 5-6 m
19
Earth, after 10 years of operation
10-3 10-2 10-1 100 101 102 10310-3
10-2
10-1
100
101
102
103
104
105
10-3
10-2
10-1
100
101
102
103
104
10510m from the target
Swiss exemption limit
about 20 years
50 years
5 years6 months
10 days1 day
Fra
cti
on
of
exem
pti
on
lim
its
Sp
ecif
ic a
cti
vit
y (
Bq
/g)
years of cooling
2-3 m from the concrete
20
Radioactivity in molasse
• There is the risk that the radioactivity in the earth may leach into the ground water.
• Radionuclides to be considered:In a soluble chemical formWith half-lives longer than 10 h
22Na, 3H
21
Radioactivity in molasse
• The radioactivity induced in the rock may leach into the ground water.
• Two possible risks:
1) Contamination of surface water
(limits on the Bq/year produced)
• 2) Contamination of public water supplies
(limits on the concentration Bq/l released)
22
Contamination of public water supplies
• Severe constraints for the concentration (Bq l-1) of activity induced in the ground water
• The estimation of the concentration of 3H and 22Na requires a hydro-geological study of the construction site
• No evaluation can be done, before the site of the facility has been chosen
23
Contamination of surface water 50 cm thick
concrete wallsAnnual release (Bq per year)
Constraint (*)
22Na 4.6·1012 4.2·1011
260 cm thick concrete walls
Annual release (Bq per year)
Constraint (*)
22Na 3.2·1010 4.2·1011
3H 7.8·1011 3.1·1015
(*) Max dose to the critical group: 0.3 mSv per year,
release constraints valid for CERN Meyrin site only
24
BetaBeams: induced radioactivity
• A large portion of the initial beam will decay during acceleration, and all injected beam is essentially lost in the decay ring
• Losses in the decay ring:~8.9 W m-1 (6He, 139 GeV/u) (*)~0.6 W m-1 (18Ne, 55 GeV/u) (*)
(*) M. Lindroos et al., Neutrino Factory Note 121
25
BetaBeams: induced radioactivityLack of data on induced radioactivity from ions
• Possible ways of estimating the material activation:
1) For high-energy particles, an A-nucleus can be approximated by A single protons (It is the easiest way to obtain a first estimation)
2) At GSI, people are working on the implementation of a code, which deals with transport and fragmentation of heavy ions
3) A new version of FLUKA is being implemented
26
Conclusions
• Even if it is not correct to simply scale the induced radioactivity produced in the decay tunnel (~kW/m) to that produced in the decay ring (~W/m), the latter is expected to be much lower than the former.
• A good estimation of the induced radioactivity in the decay ring requires a detailed study, possibly using both the simplified model and a Monte Carlo code, if available.