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Transcript of 1 Scale Detection in Geothermal Systems The use of nuclear monitoring techniques E. Stamatakis a,b,...
1
Scale Detection in Geothermal Systems
The use of nuclear monitoring techniques
E. Stamatakisa,b, T. Bjørnstadb, C. Chatzichristosb,
J. Mullerb and A. Stubosa
aNational Centre for Scientific Research Demokritos (NCSRD), Athens, Greece
bInstitute for Energy Technology (IFE), Kjeller, Norway
2
Nuclear experimental methods Gamma transmission experiments
Method Typical results
Gamma emission (tracer) experiments Method Typical radiotracer results
Outline
3
Nuclear based methods
1. Gamma emission based on radioactive tracers added to the flowing and reacting system
2. Gamma transmission based on use of external gamma sources
4
Principles of gamma transmission
x
Gamma source Gamma detector
Absorption sample
Transmission of a mono-energetic beam of collimated photons through a simple absorption sample can be described by Lambert-Beer’s equation x
ox eII is the linear mass absorption coefficient with dimension L-1 (cm-1), x the sample thickness
Io Ix
5
Mass absorption coefficientA quantity more commonly found tabulated is the mass absorption coefficient / with dimension cm2/g. In a composite sample the attenuation is additive according to
)22
( ,,,
m
Ca
CamCa
Al
AlmAl
m
xxx
ox eII
XAl XCa Xl XCa XAl
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E (keV) Iabs(%)
80.998 0.008 34.0 0.3
276.397 0.012 7.16 0.07
302.851 0.015 18.3 0.1
356.005 0.017 62.0 0.8
383.851 0.020 8.9 0.1
133BaThe gamma source used in the present experiment is 133Ba due to suitable energies (see table below) and half-life (10.5 y). Main gamma-ray energies and intensities for 133Ba are:
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Preliminary lab. experiments
1 0.7 160 15 1
2 1.5 160 15 1
3-6 20 185 10 1
RUN SR Temp.C
Pres.bar
Flowr.ml/min
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Results from “Run 1”
4350
4400
4450
4500
4550
4600
0 6 12 18 24 30 36 42 48
time (hours)
cou
nt-
rate
(cp
s)
background
Gamma attenuation measurements for calcite
precipitation at the inlet of the tube at 160oC, 15 bars and
SR=0.7 (run 1)
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Results from “Run 2”
4350
4400
4450
4500
4550
4600
0 5 10 15 20 25 30
time (hours)
cou
nt-
rate
(cp
s)
tindback-
ground
Gamma attenuation
measurements for calcite
precipitation at the inlet of the
tube at 160oC, 15 bars and SR=1.5
(run 2)
12
Results from “Runs 3-6”
Gamma attenuation measurements for
calcite precipitation in the presence and absence of a scale
inhibitor 10cm from inlet of the tube at 185oC, 10 bars and SR=1.5 (runs 3-6)
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Calcite growth rate
0
0,050
0,100
0 5 10 15 20 25
Time (hour)
Sca
le t
hic
kne
ss (
cm)
0,125
0,025
0,075
Scaling rates (scale thickness as a function of time) of calcite precipitation at the inlet of the tube for run 2 - preliminary results
0,150
0,175
0,200
0,225
0,250
0,275
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Calcite distribution across the tube
0,00
0,10
0,20
0,30
0,40
0,50
0,60
0,70
0,80
0,90
1,00
0 10 20 30 40 50 60Position (cm)
scal
e th
ickn
ess
(cm
)
5000
5200
5400
5600
5800
6000
6200
6400
6600
6800
7000
0 10 20 30 40 50 60
Position (cm)
cps
background
final
Scale thickness distribution across the
tube at the end of run 3
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The 133Ba-source (30 mCi or 100 MBq) gives a typical counting rate of about 4500 cps (counts per second) in tube filled with water (ID = 10 mm) with a detector collimator opening of 4.5x4.5 mm.
The brine-filled tube reduces the normalized incident intensity from 1.000 to 0.891when corrected for the Al-metal walls.
The increased mass thickness (g/cm2) due to scale obviously leads to an increased attenuation and to a reduction in contrast towards mass changes during the experiment.
Transmission experiments may be used to study calcite scaling in open tubes with the dimensions used here.
Discussion on -transmission
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Principles of the -emission method• CaCO3 scaling may be studied by radio-
labeling of any of the chemical components involved.
• However, for on-line, continuous and non-intrusive detection, gamma-ray emitters are required.
• Neither O nor C have suitable gamma-ray emitting isotopes.
• Ca has only one suitable radioactive isotope, namely 47Ca, with a half-life of 4.54 days.
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• The main gamma energy of 47Ca is 1297 keV. However, by including also its Compton background and lower energies in the counting window, the sensitivity in the experiment may be increased.
• It is necessary to avoid contribution from the 159 keV γ-quanta of the daughter radionuclide 47Sc.
• The energy window for the detectors will therefore be chosen from 350 keV and upwards.
On-line detector setup
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• Samples are also collected periodically at the exit end of the sandpack and the activity of 47Ca (1297 keV) in solution is determined in off-line high-resolution gamma-spectrometric measurements with a HpGe-detector coupled to a multichannel analyzer.
• Solution temperature Ts, differential pressure Δp, pH, absolute system pressure p and 47Ca2+ activity (counting rate R) from the two on-line detectors are logged by computer during the experiment.
Other measured parameters
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Typical tracer results (1)
0
10
20
30
40
50
60
70
80
0 20 40 60 80 100 120 140
Time (min)
cps
tind
scales
47Ca background
Add NaHCO3
Environmental background
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Typical tracer results (2)
Typical results from a previous experiment with higher SR:
47Ca deposit growth at the inlet and Δp buildup along the
tube vs. time
0
25
50
75
100
125
150
175
200
0 20 40 60 80 100 120 140
Time (min)
cou
nt-
rate
(cp
s)
0,0
0,2
0,4
0,6
0,8
1,0
Δp
(b
ar)
Ca(47) tracer backgroundΔp
47Ca deposit growth in the presence and absence of a
scale inhibitor
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Typical tracer results (3)
012
345678
91011
0 5 10 15 20 25 30 35 40 45 50 55 60
Position (cm)
cou
nt-
rate
(cp
s)
total Ca(47)
initial Ca(47)
final Ca(47)
precip. Ca(47)
0
2
4
6
8
10
12
0 20 40 60
Position (cm)
mg
r C
aC
O 3
Final distribution of the deposits across the tube
0
1
2
3
4
5
6
7
8
9
10
11
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14
Position (cm)
cou
nt-
rate
(cp
s)background Ca(47)
0-30 min
30-60 min
60-90 min
90-120 min
120-150 min
after 4 hours
47Ca deposit distribution across
the tube at different time-steps
24
Discussion on -emission
The radiotracer 47Ca can be used to study CaCO3 precipitation in tube blocking tests providing the following unique information:
The induction time of CaCO3 scale deposition
Visualization of the spatial distribution (concentration versus position) of the CaCO3 scale deposition
All experiments with tracers showed that the tracer monitoring gives a shorter induction time than monitoring of the pressure dropA novel technique for the determination of MIC, based on the γ-emission method, can be developed.
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Final Conclusions Both methods are capable to visualize the
distribution of the scale deposits, a result that is not readily obtained by methods commonly used in conventional dynamic scaling experiments.
The techniques are sensitive to scaling, resulting generally in shorter induction times compared to Δp-monitoring.
The methodologies can be easily used for the laboratory investigation of the scaling processes occurring in geological systems, including oilfield, geothermal and hydrology applications and for all kind of mineral scales.
Their results are meant to be applicable at the field scale; the quantification of the earlier occurrence of scale precipitation that those techniques attain can be directly implemented in large scale simulators.