industrial application of radioisotopes in zimbabwean industries€¦ · 28-04-2017 · industrial...
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Industrial application of radioisotopes
in Zimbabwean industries Peter Baricholo
National University of Science and Technology, Department of Applied Physics, P. O. AC939, Ascot, Bulawayo, Zimbabwe
www.nust.ac.zw
VIC, Vienna, Austria, 24 – 28 April 2017
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Introduction
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VIC, Vienna, Austria, 24 – 28 April 2017
Zimchem Refineries
Group Members Dr. B. Muchono Mr R. T. Mashingaidze Mr W. Chirume Mr. C. Dzingai Eng. S. Mudono
Outline
• Introduction
• RTD experiment at PPC
• RAF1004 Final coordination meeting
• Environmental Gamma Radiation Monitoring at Power Plant
• NDT activities
• Preparations for Gamma column scans
• Conclusions
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VIC, Vienna, Austria, 24 – 28 April 2017
Raw mill 13.5m long and 4.2m in diameter at the factory
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VIC, Vienna, Austria, 24 – 28 April 2017
RTD Experiment at PPC
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RTD Experiment at PPC Radiotracer preparation
• The preparation of the radioactive tracer was conducted in a laboratory
at PPC Colleen Bawn.
• The radioactivity was of approximately 200 mCi in solid metal form of 198Au.
• To prepare the solid 198Au; an acid solution composed of 1 part of
concentrated HNO3 by volume and 3 parts of concentrated HCl by
volume was used.
• Aqua Regia solution which was allowed to react for approximately 30 min
to form a yellow solution to that it dissolves metal gold.
• The gold in metal form was submerged into the solution and allowed to
stand for an hour to dissolve.
• After the gold was dissolved, it was further diluted with ethanol to a
volume of 80 ml.
VIC, Vienna, Austria, 24 – 28 April 2017
RTD Experiment at PPC
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Experiment 1: 1 kg of limestone with 40 ml of the gold solution with a total
activity of app. 100 mCi 198Au tracer. The material feed rate was 90 t/h.
Experiment 2: 1 kg clay with 20 ml solution with app. 50 mCi of 198Au. The
material feed rate was 90 t/h.
Experiment 3: 1 kg of limestone labelled with 20 ml solution with an
activity content of appx. 50 mCi of 198Au. The feed rate was 85 t/h.
Concentration of tracer using sensitive scintillation detectors placed at
appropriate positions along the mill system as a function of time was
recorded.
VIC, Vienna, Austria, 24 – 28 April 2017
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Radiotracer was introduced to the end of the raw material conveyor belt, with
the three detectors placed in three different zones, i.e.:
Detector D1: at the mill inlet for recording the zero time of tracer entering the
mill,
Detector D2: at the mill outlet,
Detector D3: at the separator outlet for recording the material that returns to
the mill entry for regrinding.
RTD Experiment at PPC
VIC, Vienna, Austria, 24 – 28 April 2017
0
5000
10000
15000
20000
25000
30000
35000
40000
0 250 500 750 1000 1250 1500
Recirculation
Output pulse
Co
un
tsp
er s
eco
nd
Time in seconds
Limestone (Flow rate = 90 T/hr)
Experiment 1
Experiment 2
The mean residence time through the mill
was calculated as 8.27 min and can be
considered as representative.
The mean residence time from the inlet
pulse to the detector on the recycle line is
8.74 min.
The MRT of the clay is much quicker than that
of limestone, which can be attributed to the
particle size which creates less resistance
against the material flow and grinding process.
RTD experimental results
VIC, Vienna, Austria, 24 – 28 April 2017
The MRT at outlet of mill is
3.36 min, and the transit
time of the material from
the outlet of the mill to the
recycle line is 2.14 min. 8
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0
5000
10000
15000
20000
25000
30000
35000
0 250 500 750 1000 1250
Output pulse
Recirculation
Co
un
ts/s
Time/s
Limestone (Flow rate = 85 T/hr)
Experiment 3
RTD experimental results
The MRT from the inlet
of the mill (40.9s) to the
outlet (330.83s) is
relatively fast at 4.83
min, in comparison with
90t/h (8.27min).
Results show that the grinding process of raw materials inside the mill is not optimal; it
seems that:
1. the dynamic behaviours of limestone and clay are different, clay spends less time
inside the mill compared to limestone (for the same regime),
VIC, Vienna, Austria, 24 – 28 April 2017
2. clay dynamics inside the mill was abnormal; there was a portion
of clay particles that moves faster from the input to the exit
bypassing the grinding process (or short-circuit).
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RAF1004 Final Coordination Meeting
VIC, Vienna, Austria, 24 – 28 April 2017
Environmental Gamma Radiation Monitoring at Power Plant
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Onsite monitoring stations at the thermal power station.
VIC, Vienna, Austria, 24 – 28 April 2017
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Experimental set up for taking measurements on raw coal.
Experimental set up for
taking measurements on
fly ash and bottom ash mixture.
Radon monitoring in coal and fly ash of a small thermal power plant
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0
50
100
150
200
250
300
0 100 200 300 400 500 600 700 800 900
Ac
tivit
y (
cp
s)
Time (s)
Detector 1 on Ash
Detector 2 on Ash
Detector 1 on coal
Detector 2 on coal
0
50
100
150
200
250
1 2 3 4 5
Acti
vit
y (
cp
s)
Day of experiment
Ash
Coal
Average activity
of raw coal and
ash for 5 days
Activity of raw coal and ash
measured on 18/03/2016
Radon monitoring in coal and fly ash of a small thermal power plant
VIC, Vienna, Austria, 24 – 28 April 2017
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NDT Activities
VIC, Vienna, Austria, 24 – 28 April 2017
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Gamma Column Scanning Activities
Zimchem Refineries
Zone zero refinery
Plant process Crude Benzole and Crude Tar
VIC, Vienna, Austria, 24 – 28 April 2017
• Zimchem was formed in 1989
and the refinery was
commissioned in 1993.
• The refinery produces Crude
Benzole and Crude Tar used to
manufacture Road Tars, Pitch,
Coal Tar Fuels, Heavy Furnace
Fuels, Creosote (a wood
preservative) and industrial
solvents such as Benzene,
Toluene Xylene and
Naphthalene.
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We are currently in the
process of preparing to
carry out the gamma column
scanning experiment at the
refinery.
Gamma Column Scanning Activities at Zimchem Refineries
VIC, Vienna, Austria, 24 – 28 April 2017
Some of the solvents are
used to make a wide range
of industrial chemicals and
detergents, such as
thinners, Contact Adhesives, Agrochemicals, etc.
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