1.
Introduction
1.1 Sources of background radiation
Human
beings constantly and all along are exposed to ionising radiations exiting in
nature. These natural background
radiations have both terrestrial and extraterrestrial origin. The extraterrestrial radiation is largely due
to cosmic rays. Earth's atmosphere is continuously bombarded with high energy
cosmic rays which originate from our own cosmos. The primary interaction of high energy cosmic
rays with the atmosphere produce numerous secondary radiations in the form of
neutrons and protons of various energies which in turn produce a variety of
radionuclides through nuclear reactions with nitrogen, oxygen and other nuclei
in atmosphere and through other processes.
In addition, sub atomic particles like mesons, muons and electrons are
also produced.
The
terrestrial sources of radiation can be divided into those that occur singly
and those that are components of the three chains of radioactive series namely
the uranium series, the thorium series and the actinium series. Among the
singly occurring radionuclides Potassium-40 with half life of 1.3X109
years is the most prominent one and it is widely distributed in rocks and
soil. The radionuclide Rubedium-87 which
is another singly occurring radionuclide is of secondary importance. 40K is fairly abundent forming
about 0.012% of total K, and is widely distributed in environmental
martix. Moreover, K is an essential
element for most life forms. In
addition, 40K contributes significantly to gamma radiation in the
environment. No significant
fractionation of 40K takes place in the environment so that the
radioactivity of 40K is almost constant under
all conditions. Since the abundance of 40K is
0.012%, 1 kg of soil contains about 2.36 mg of radioactive 40K.
Uranium-238
and Thorium-232 and their daughters generate the bulk of natural ionising
radiation in our environment.
Uranium-238 is the head of a series of 15 principal radionuclides . It is the most abundant (99.28%) isotope of
natural uranium and is found in all rocks and soil with varied concentration.
The 238U decays through 234U and 230Th to 226Ra,
which has a relatively long half life of 1628 years. 226Ra and its daughter products
constitute an important part of natural radiation exposure. About 98% of the external dose from uranium
series is delivered by 226Ra and its daughter products. The 226Ra
is distributed in soil in varying concentration. Its concentration in soil of normal
background region varies from 2.59 Bq kg-1 to 140.6 Bq kg-1
covering two orders of magnitude, because of the wide range of soil
characteristics.
The
other major source of terrestrial radiation is 232Th and its decay
products. Thorium-232 is the only long lived radionuclide in its chain and is
widely distributed in rocks and soil in varied concentration. The 232Th content of igneous rocks
is about four times the uranium content, but since the specific activity of 232Th
is 2.97 Bq g-1 compared to 8.92 Bq g-1 238U,
the radioactivity due to the two nuclides is nearly 1:1. The 232Th (T1/2=1.4X1010
years) decays to 228Ra (T1/2 = 5.76 years) by alpha emission. Radium-228 is a beta emitter and has
considerable significance in environmental radioactivity studies. All the daughters of 228Ra are
short lived. One of the daughter
products 220Rn, is a radioactive gas. But it has short half life 55 sec. and therefore
the emanation of 220Rn is significantly less compared to 222Rn.
The
radioactive decay of 40K and radionuclides of 238U and 232Th
series give rise to the terrestrial gamma rays.
The average outdoor terrestrial absorbed dose rate in air from gamma
radiation was found to be 44 nGy h-1 and the relative contribution
of 40K, 238U and 232Th are about 35%, 25% and
40% respectively (UNSCEAR 1982). There are regions in the world where the out
door terrestrial radiation exceed substantially from the normal variability
ranges due to the enrichment of certain radioactive minerals leading to the
formation of what are known as high background areas. The presence of high
background areas have been reported in several countries like China , Iran , Germany , USA , Brazil and India .
1.2 Artificial radionuclides
The open air nuclear weapon tests and operation of nuclear power
reactors are the major sources of artificial radionuclides. Among the several hundred radionuclides
produced by nuclear explosions, only 90Sr(T1/2=28.6
years), 137Cs(T1/2=30.2 years) and 131I((T1/2=131
days) contribute significantly to human exposure.
2. Objectives
The research programme envisaged in this project have
following objectives:
- To evaluate the gamma radiation
dose to the population of Udupi district
- To measure the concentrations of 226Ra,
232Th and 40K in soil/sand and
- To calculate the contribution of
cosmic radiation to the radiation dose received by the population
3. Results:
3.1 Dosage
Rates:
Udupi Taluk
Table-1
Sl
No
|
Place
|
|
1
|
Physics
Department
|
14.
|
2.
|
College
Ground
|
12
|
3
|
Kallianpur
|
12
|
4
|
Near
|
12
|
5
|
Doopada
Katte(Brahmavar)
|
10
|
6
|
Brahmavar(
Brahmavar Chemicals)
|
10
|
7
|
UppinaKote
|
11
|
8
|
Mabukala
( Near River)
|
8
|
9
|
Saligrama
|
8
|
10
|
8
|
|
11
|
Bannadi
|
10
|
12
|
Girike
Mata
|
11
|
13
|
Saibra
Katte
|
12
|
14
|
Barkur
|
10
|
15
|
Yedthady
|
18
|
16
|
Near
Mandharthi
|
24
|
17
|
Mandharthi
|
11
|
18
|
Kadoor
|
10
|
19
|
Kokkarne
|
12
|
20
|
Sural
|
12
|
21
|
Amuje(Karje)
|
9
|
22
|
Kannaru(Near
Karje)
|
14
|
23
|
Petri
|
13
|
24
|
Cherkadi
|
11
|
25
|
Ammuje
(Near Karje)-2
|
9
|
||
26
|
Chantharu
|
10
|
||
27
|
Brahmavar(Near
West Cost Chemicals)
|
13
|
||
28
|
Kolalgiri
|
12
|
||
29
|
Tenkabettu
|
13
|
||
30
|
SubasNagar
|
13
|
||
31
|
Pajaka
|
13
|
||
32
|
Padubelle
|
13
|
||
33
|
Manasa
|
13
|
||
34
|
B.C
Road
|
10
|
||
35
|
Manchakkal
|
11
|
||
36
|
Bantakkal
|
10
|
||
37
|
Shankarpura
|
12
|
||
38
|
Katpady
|
12
|
||
39
|
Nittur
|
12
|
||
40
|
Puttur
|
8
|
||
41
|
Kodavur
|
11
|
||
42
|
8
|
|||
43
|
7
|
|||
44
|
11
|
|||
45
|
Tottam
|
10
|
||
46
|
Badanidiyur
|
9
|
||
47
|
Gujjar
Bettu
|
8
|
||
48
|
8
|
|||
49
|
Kemmannu
|
11
|
||
50
|
Kelarkalabettu
|
11
|
||
51
|
Kaup
Light House
|
12
|
||
52
|
9
|
|||
53
|
Uchila
|
13
|
||
54
|
Padubidri
|
8
|
||
55
|
Nandikur(Nagarjuna)
|
12,
|
||
56
|
Hiriyadka
|
12
|
||
57
|
Athrady
|
13
|
||
58
|
Parkala
|
12
|
||
59
|
Manipal(End
Point)
|
12
|
||
60
|
Perampalli
|
14
|
||
Dosage
Rate -- Karkala Taluk Table
2
Sl
No
|
Place
|
|
1.
|
Santhoor
|
10
|
2
|
Belman
|
11
|
3
|
Kedinge
|
10
|
4
|
Nitte
|
9
|
5
|
16
|
|
6
|
Attur
Hill
|
13
|
7
|
Anekere
|
10
|
8
|
Gomateshwara
Hill
|
14
|
9
|
Kukkundoor
|
10
|
10
|
Jarkala
|
14
|
11
|
Bailur
|
13
|
12
|
Guddeyangadi
|
13
|
13
|
||
Dosage
Rate in Kundapur Taluk Table 3
Sl
No
|
Place
|
|
1
|
Koteshwar
|
8
|
2
|
Kundapur
|
8
|
3
|
Tallur
|
9
|
4
|
Gangolli
|
13
|
5
|
Maravanthe
beach
|
6
|
6
|
13
|
|
7
|
Navunda
|
8
|
8
|
Kambadakone
|
9
|
9
|
Byndoor
Hill(Road)
|
12
|
10
|
Byndoor
Hill top
|
11
|
11
|
Byndoor
Hill Down
|
10
|
12.
|
10
|
|
13
|
Someshwar
beach Water
|
7
|
14
|
Someshwar
temple
|
9
|
3.2: Radio Nuclides in Soil Samples.
Table 4. Udupi Taluk
Place
|
K-40
|
Cs-137
|
Th-232
|
Ra-226
|
Pb-210
|
||
1. Kodavoor
|
21.894±1.22
|
15.726±0.10
|
7.759±0.291
|
10.484±0.272
|
14.303±1.889
|
||
2. Cherkady
|
65.754±1.98
|
BD
|
13.460±0.355
|
7.837±0.255
|
5.004±1.89
|
||
3.Kakkunje
|
33.495±1.55
|
BD
|
11.334±0.33
|
12.119±0.28
|
14.098±2.004
|
||
4.Karje
|
152.97±3.144
|
1.302±0.11
|
4.594±0.255
|
1.882±0.203
|
17.01±1.83
|
||
5.Kukke Halli
|
35.3±1.50
|
0.1798±0.108
|
8.069±0.287
|
6.39±0.24
|
6.04±1.707
|
||
6.Dupadakatte
|
37.348±1.62
|
B.D
|
15.497±0.38
|
13.255±0.30
|
9.477±2.09
|
||
7.Kemmannu
|
109.95±2.54
|
1.223±0.116
|
5.668±0.262
|
3.849±0.211
|
16.179±1.819
|
||
8. Barhmavar Sugar Factory
|
31.011±1.489
|
5.437±0.074
|
8.722±0.300
|
10.130±0.277
|
20.590±2.080
|
||
9.Kallianpur
|
57.139±1.920
|
BD
|
14.360±0.368
|
16.450±0.328
|
14.573±2.16
|
||
10.Pamboor
|
59.840±1.930
|
BD
|
12.939±0.354
|
10.420±0.270
|
8.620±2.060
|
||
11.Shivally
|
55.147±1.840
|
0.724±0.131
|
11.673±0.341
|
16.54±0.319
|
20.682±2.17
|
||
12.Nejar
|
58.430±1.960
|
BD
|
15.430±0.380
|
19.060±0.34
|
22.53±2.44
|
||
13. Tenkanidiyur
|
73.467±2.70
|
BD
|
8.879±0.306
|
5.908±0.248
|
5.839±1.850
|
||
14. Hebri (Near Karje)
|
61.677±2.540
|
BD
|
24.177±0.520
|
14.830±0.369
|
13.437±2.870
|
||
15. Yedthady
|
41.780±1.598
|
BD
|
6.504±0.270
|
6.521±0.234
|
7.201±1.950
|
||
16. Kukkehalli North
|
43.130±1.697
|
0.453±0.119
|
10.115±0.309
|
8.286±0.260
|
9.920±0.260
|
||
17. Kokkarne
|
28.050±1.426
|
2.177±0.127
|
11.264±0.323
|
5.819±0.237
|
30.360±2.060
|
||
18.Hebri
Nisargadama
|
80.040±2.190
|
BD
|
14.865±0.368
|
96.850±0.283
|
10.110±1.970
|
||
19. Perampalli
|
27.833±1.480
|
3.870±0.167
|
12.200±0.349
|
14.666±0.3110
|
15.090±2.100
|
||
20. Herror
|
39.940±1.590
|
3.322±0.149
|
10.250±0.319
|
16.540±0.319
|
20.680±2.170
|
||
21.Cherkady
|
82.120±2.510
|
1.150±0.160
|
17.100±0.449
|
8.389±0.311
|
13.490±2.46
|
||
22.Malpe Sand
|
95.003±2.580
|
BD
|
0.950±0.220
|
1.05±0.180
|
BD
|
||
23. Hoode sand
|
35.830±1.990
|
BD
|
37.730±0.670
|
17.460±0.420
|
11.37±3.540
|
||
24. Nandikoor
|
51.330±2.014
|
BD
|
2.058±0.479
|
6.540±0.296
|
14.530±2.370
|
Radio
Nuclides in Soil Samples of Karkala
Taluk
Table--5
Place
|
K-40
|
Cs-137
|
Th-232
|
Ra-226
|
Pb-210
|
||
1Nakre
|
66.30±2.06
|
BD
|
36.83±0.548
|
12.07±0.32
|
6.18±1.889
|
||
2. Ajekar
|
92.09±2.45
|
BD
|
47.36±0.629
|
22.23±0.39
|
17.39±3.00
|
||
3.Karkala
|
66.88±2.06
|
BD
|
17.67±0.39
|
15.62±0.39
|
12.99±2.41
|
||
4.Bailur
|
138.36±2.978
|
0.534±0.126
|
13.62±0.36
|
9.81±0.278
|
19.10±2.32
|
||
5.Nitte
|
68.13±2.01
|
1.07±0.121
|
11.311±0.335
|
8.657±0.268
|
9.32±1.86
|
Radio
Nuclides in Soil Samples of Kundapura
Taluk
Table
6
Place
|
K-40
|
Cs-137
|
Th-232
|
Ra-226
|
Pb-210
|
Th-234
|
|
22.38±1.49
|
BD
|
0.622 ±0.218
|
13.52±2.25
|
BD
|
|||
2.
|
55.07±1.99
|
BD
|
1.378±0.218
|
1.047±2.07
|
4.88±1.51
|
||
3.Kambadakone
|
41.945±1.61
|
BD
|
0.280±0.105
|
9.519±0.308
|
7.54±0.25
|
8.58±1.83
|
|
4.Tallur
|
62.78±1.97
|
BD
|
16.89±0.394
|
16.43±0.329
|
BD
|
17.58±2.41
|
|
5.Gangolli
|
41.76±1.59
|
BD
|
6.503±0.27
|
6.521±0.234
|
7.20±1.95
|
6.44±1.78
|
|
6Byndoor Hill
|
3.85±1.00
|
B.D
|
5.069±0.259
|
4.678±0.211
|
7.017±1.51
|
5.508±1.36
|
5. Analysis and conclusions:
We can see from
Table1, Table 2 and Table 3 that average dosage rate people receive is quite
normal. Only at Yedthady , Mandarthi and miraculous pond of Attur church the
activity slightly high but at normal rate. The higher activity could be due to the
presence of thorium in the granite.
Dosage rate at the beaches of Udupi district is quite low compared to hilly
reagion. So there is no posibility of thorium content like Kerala or Ullal beach.
( Siddappa et all )
Table 4, Table 5
and Table 6 show that Radio Nuclide K-40 is present in all the soil samples in
good amount and this radio nuclede is the main source which contributes for the
sose rate that the people of udupi district receive. The value is quite high in
Kemmannu and Karje area.
The isotope cs-137 is present in very small
quantity and almost BD in all the soils. Hence the contribution of this nuclide
is negligible in the Udupi district.
The Radio
isotopes Th-232, Ra-226, and Pb-210 are present in all the soil samples in a
small quantity.
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