ISSN 0972-0464
Radiation Protection and Environment • Volume 41 • Number 4 • October-December 2018 • Pages ***-***
Radiation
Protection and
Environment
Volume 41 / Issue 4 / October-December 2018
Publication of INDIAN ASSOCIATION FOR RADIATION PROTECTION (IARP)
www.iarp.org.in
Review Article
Review on studies in natural background radiation
Abdu Hamoud Al-Khawlany1,2, A. R. Khan3, J. M. Pathan1
Departments of 1Physics and 3Computer Science, Maulana Azad College, Dr. Babasaheb Ambedkar University, Aurangabad, Maharashtra,
India, 2Department of Physics, Faculty of Education and Languages, Amran University, Amran, Yemen
Abstract
The environment around us is radioactive due to background radiation emitted from the sky, earth’s crust,
food, water, and building materials. The human body gets exposed to radiation doses of about 82%, which
are out of control; they arise from background radiation sources such as terrestrial, cosmic, and exposure to
internal radiation. The background dose from cosmic radiation depends on the altitude, and regions with high
altitude have high radiation doses. Natural radioactivity is present in the earth and is present in the different
environment geological formations in the rocks and soils. Gamma radiation emitted from naturally occurring
radioisotopes, such as 40K and the radionuclides from the 232Th and 238U series and their decay products
which exist as trace levels in all ground formations, represents the main external source of irradiation to
the human body. Their concentrations in rocks, soils, and sands depend on the local geology of each region
in the world. Naturally occurring radioactive materials have terrestrial-origin radionuclides since the creation
of the earth. The dose rate of background radiation increases because of the existence of some quarries and
springs in some regions which are called high-level background radiation regions. The type of construction
materials used in houses can be affecting the dose rate of background radiations. Study of radioactivity in the
environment is important to monitor the levels of radiation to which human is exposed directly or indirectly.
Recently, several international studies have been done and different values were measured. In this article, a review
and literature survey of background radiations such as terrestrial, cosmic, and food radiation was carried out.
Keywords: Background radiation, cosmic rays, dose rate, environment, radioactivity
Address for correspondence: Mr. Abdu Hamoud Al‑Khawlany, Department of Physics, Maulana Azad College, Dr. Babasaheb Ambedkar University,
Aurangabad ‑ 431 001, Maharashtra, India.
E‑mail: abdu.alkhawlany@gmail.com
Submission: 17‑Jul‑2018 Revision: 13‑Oct‑2018 Accepted: 30‑Nov‑2018
INTRODUCTION
The human population is exposed to radiation continuously,
which comes from various diverse sources. Some of these
sources are natural, and others are the result of human
activities. The radiation from natural sources includes
cosmic radiation, external radiation from radionuclides in
the earth’s crust, and internal radiation from radionuclides
inhaled or ingested and retained in the body. The
amount of natural radiation exposures depends on
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geographical location, geological formations, and some
human activities. Height above the sea level affects the
dose rate from cosmic radiation.[1] Natural radionuclides
are present in the earth environment, and they exist in
different geological formations such as earth’s crust, air,
soils, rocks, water, and plants. The environment when
exposed to harmful substance can become polluted,
thus producing harmful effect to human and other biotic
organisms in the environment. Radionuclide sources
cause pollution in the environment if allowed to build up
due to natural occurrence or anthropogenic activities.[2]
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DOI:
10.4103/rpe.RPE_55_18
How to cite this article: Al-Khawlany AH, Khan AR, Pathan JM. Review on
studies in natural background radiation. Radiat Prot Environ 2018;41:215-22.
© 2019 Radiation Protection and Environment | Published by Wolters Kluwer ‑ Medknow
215
Al-Khawlany, et al.: Review on studies in natural background radiation
Natural radioactivity is common in rock formations and
soil that make up our planet earth, in waters and oceans,
and in building materials everywhere. Monitoring of
natural background radiation is important to humankind,
and environmental protection studies on radionuclide
concentration variation with geological formation, soil
type, and depth profiles are relatively new in the field of
radiation and radioactivity concentration studies in the
environment.[3] Therefore, the study information and
survey of natural environmental radiation are of great
importance and interest in health physics, not only for many
practical reasons, but also for more fundamental scientific
reasons. [3,4] The earth’s crust contains radionuclides
which constitute the major source of naturally occurring
radioactive materials (NORMs) in the environment. Most
of these radionuclides are members of the radioactive
decay series, 238U, 235U, and 232Th. The members of these
chains undergo radioactive decay, which is a spontaneous
process in which a radioactive nucleus transmutes into
one or more constituent elements, eventually decaying
into a radioactively stable isotope. The change from the
“parent” nuclei into a different element or “daughter”
nuclei is also referred to as nuclear transmutation, which
is usually accompanied by the emission of alpha and/or
beta particles. According to the UNSCEAR, 2000,[5] there
exist about 340 naturally occurring nuclides, of which about
70 are radioactive and are found mainly among the heavy
elements, with A >200.
The earth is exposed to ionizing radiation and as a result,
radioactive materials can be found in our foods, soil, air,
water, and building materials.[6,7] The human body contains
radionuclides such as 40K and 14C. Radiation is ubiquitous
and thus exposure to gamma‑ray‑emitting radionuclides
cannot be completely avoided.[8] Every day, we are exposed
to radiation of different kinds originating from different
sources. We receive radiation exposure from cosmic rays,
outer space, radon gas, and from other natural radioactive
elements in the earth. This radiation is called natural
background radiation including the radiation we get from
plants, animals, and from our own bodies. Furthermore,
we are exposed to radiation from human‑made sources
such as medical and dental treatments, television set, and
emission from coal‑fired power plants. This research aims
to survey and implement a radiometric analysis for several
international studies to provide data and baseline map of
radioactivity background level in the environment. This
can be used as reference information to assess any changes
in the radioactive background level due to geological
processes. The present study contributes immensely to the
understanding of the characteristics of natural background
radiation.
216
Sample preparation
Samples such as rock and soil were taken from the study
areas and then crushed into small pieces and ground to
powder of suitable powder size. Each sample was dried
in an oven at 105°C or suitable temperature and sieved
through appropriate mesh for optimum size minerals. The
sample was packed in suitable plastic container. The sample
was weighed and stored for a minimum suitable period
of 1 month to allow the daughter product to come into
radioactive equilibrium with their parent 226Ra and 232Th and
then counted for 8–12 h depending on the concentration
of radionuclide.
Radiometric counting and data analyses
One of the most valuable techniques for low‑level
radioactivity measurements is gamma‑ ray spectrometry.
The various systems, consisting of scintillation and
semiconductor detectors coupled to multichannel
analyzers, provide for rapid simultaneous measurement of
many radionuclides in the same sample. HPGe detector is
preferred for the determination of radionuclides in food
and environmental samples because of the higher resolving
power (energy resolution = full width at half maximum)
of the HPGe detector than that of the NaI (Tl) detector;
high‑energy resolution is essential for the analysis of
the complex γ‑spectra. NaI (Tl) scintillation is preferred
when high‑energy resolution is not essential. The energy
resolution of NaI (Tl) crystal (3” × 3”) is about 6% for the
photopeak of 137Cs at 661.6 keV (i.e., it is about 40 keV)
and about 60 keV for the photopeak of 60Co at 1332 keV,
whereas the energy resolution of HPGe detectors is about
1.9 keV for the photopeak of 60Co at 1332 keV. The energy
calibration of HPGe detector or NaI (Tl) scintillation
detector system should be made by measuring standard
sources of known radionuclides with well‑defined energies
within the energy range of interest, usually 60–2000 keV. To
measure the main natural gamma‑ray emitters by NaI (Tl),
the efficiency should be known at least from 239 (212Pb)
to 2614 keV (208Tl).
The measurement apparatus has to be properly shielded
with a lead cover in order to limit the environmental
radioactivity impact. Among the natural radionuclides of
interest for radiation protection issue, only 40K is directly
measurable by gamma spectrometry through its photopeak
at 1460.83 keV, characterized by an emission probability
of 10.67%. 238U is not easy to detect by gamma‑ray
spectrometry due to the low energy and emission
probability of the photopeaks of its first‑decay products.
However, since in the 238U series, approximately 98.5%
of the radiological effects is engendered by 226Ra and its
progeny, the specific activity of 238U could be assumed to
Radiation Protection and Environment | Volume 41 | Issue 4 | October-December 2018
Al-Khawlany, et al.: Review on studies in natural background radiation
be equal to that of 226Ra, neglecting its precursors.[9] 226Ra
can be detected by its photopeak at 186.1 keV directly,
also can be measured indirectly by taking into account
of 222Rn decay products, for example, 214Pb (photopeak
at 351.93 keV, with an emission probability of 35.1%) or
214
Bi (609.31 keV, 44.6%). In this case, secular equilibrium
between radon and its daughters must be ensured. Gamma
spectrometry is not sufficiently efficient to directly measure
the photopeaks of 232Th since they are characterized by
low energy and emission probability. For this reason,
the photopeaks of some of its decay products, such as
228
Ac (911.2 keV, 25.8%), 212Pb (238.63 keV, 43.3%), or
208
Tl (583.19 keV, 30.4%), should be measured with the
aim of evaluating the specific activity of 232Th. The energy
and counting efficiency calibrations are required. It is
important to maintain the same experimental conditions
of the calibration step, such as counting time, photopeaks,
volume, geometry, and position of the sample.
Counting efficiency for all the energies of interest has to
be evaluated by means of suitable standardized calibration
sources, characterized by a density near to that of the
sample. The contribution of the background has to be
evaluated by measuring a blank with the same volume
and dimensions of the sample. Moreover, a counting
time of at least 60,000 s is required to achieve better
counting statistics. The counting time of the sample has
to be chosen so as to reduce the statistical uncertainty
to obtain a reliable and accurate measure. In particular,
the counting time is governed by the radioactivity of the
sample, detector‑to‑source distance, and acceptable Poisson
counting distribution uncertainty. Finally, with regard to the
data analyses, the total net counts have to be determined
from the measured spectra, considering the Compton
continuum subtraction. Each specific activity has to be
evaluated by taking into account the mass of the sample,
blank measurement, and counting efficiency. The standard
deviation associated with each radionuclide and the lowest
detectable limit have to be evaluated.
of 59 nGy/h worldwide. The levels of natural background
radiation were increased at specific areas in some countries
like Iran, India, and Brazil, and the dose rate of 17, 28, and
90 μGy/h, respectively, will be converted into equivalent
dose using gamma radiation of unity.[11] The terrestrial
radiation sources are varying significantly from place to
place. These belonged to soil surface and building materials.
Cosmic radiation
The earth’s atmosphere is continuously bombarded with
high‑energy cosmic rays which originate from the cosmos.
The primary interaction of high‑energy cosmic rays with
the atmosphere produces a number of 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
present in the atmosphere and through other processes. In
addition, subatomic particles such as mesons, muons, and
electrons are also produced. The production rate of these
radionuclides and particles varies appreciably with both
altitude and latitude, but is relatively constant with time.
About 70% of the cosmogenically produced radionuclides
are produced in the stratosphere, while the remainder is
formed in the troposphere.[12] Moreover, the natural dose
rates from cosmic radiation depend strongly on the altitude
and slightly on the latitude. The latitude effect is due to the
charged particle nature of the primary cosmic rays, and the
effect of the earth’s magnetic field, which tends to direct
ions away from the equator and toward the poles.
DISCUSSION
The prominent radionuclides produced due to cosmic ray
interaction with the atmosphere are 3H, 7Be, 14C, and 22Na.
Beryllium‑7 is a commonly identified beryllium radioisotope
present in our environment. The ambient dose rate at sea
level due to cosmic rays is estimated to be 31.96 nGy/h for
India.[13] The UNSCEAR (2000)[5] has given a value of 31
nGy/h as the worldwide representative value for the ambient
dose due to the cosmic rays at sea level. Table 1 presents the
details of some of the important radionuclides produced by
the cosmic rays and terrestrial sources which are of interest
present in the atmospheric environment, respectively.
Terrestrial radiation
Radioactivity of building materials
Terrestrial radiation is emitted by natural radioactive
materials present in the earth’s crust in the rocks, soils,
water, air, and vegetation. These include primordial
radionuclides such as uranium, thorium, and their daughter
products such as radon and thoron. The annual effective
dose of terrestrial radiation is 0.48 mSv/y for external
exposure and 0.29 mSv/y for internal exposure to
individuals.[10] The UNSCEAR, 2000,[5] has reported that,
from terrestrial grounds, humans receive an average dose
The radioactive minerals present in the construction
materials are the main sources of gamma radiation apart
from the natural background radiation of the location.
Recently, there is a tendency to use building materials
which may contain naturally or technologically enhanced
levels of radioactivity in high‑background radiation areas.
Therefore, most of the building materials contain high levels
of primordial radionuclides and other radionuclides. Human
beings who spend more than 80% of their time in the houses
Radiation Protection and Environment | Volume 41 | Issue 4 | October-December 2018
217
Al-Khawlany, et al.: Review on studies in natural background radiation
and office buildings are exposed to radiation emitted by
the radionuclides present in the building materials.[14] For
example, the average person in the UK spends only 8% of
his/her time out of doors. We receive most gamma radiation
from building materials, while most Radon (222Rn) emits
from the ground underneath a building. Geology is the very
important factor controlling and impacting the source and
distribution of gamma radiation and radon gas, so areas of
high level of radon potential and natural radioactivity can
be mapped using geological and geophysical information.
However, the results of dose rate to the population depend
on additional factors such as soil type, house construction,
and life style.[15] The relationship between concentrations of
radon in houses and lung cancer has been analyzed in some
countries in the world such as Germany, China, Canada,
Finland, Sweden, the USA, and the UK, all these studies
indicate that higher lung cancer rates occur in people exposed
to higher levels of radon gas. Table 2 presents typical values
of NORM in constructing common building materials
used in different countries of the world, both as structural
materials and covering layers.[16,17] where granite shows the
highest range of radioactivity in building materials.
Natural radioactivity in soils and rocks
NORMs have been present in the earth’s crust since it
was formed approximately 4.5 billion years ago. These
Table 1: Natural radionuclides in the atmospheric
environment
Isotopes produced by cosmic
Isotopes produced from
rays
terrestrial sources
Isotope Half-life Radiation Isotope
Half-life
Radiation
emitted
emitted
14
C
Si
39
Ar
3
H
22
Na
35
S
7
Be
37
Ar
33
P
32
P
24
Na
32
β
β
β
β
β, γ
β
γ
γ
β
β
β, γ
5730 years
650 years
269 years
12.3 years
2.6 years
87 days
53 days
35 day
25 days
14 days
15 h
222
Rn
Po
214
Pb
214
Bi
210
Pb
210
Bi
210
Po
220
Rn
216
Po
212
Pb
212
Bi
218
α
α
β, γ
α, β, γ
β
β
α
α
α
β, γ
α, β, γ
3.82 days
3.05 minutes
26.8 minutes
19.7 minutes
20.4 years
5.0 day
138.4 days
55 s
0.158 s
10.64 h
60.6 minutes
Table 2: Range of concentration of radionuclides in common
building materials
Building material
Cement
Tiles
Bricks
Ceramics
Gypsum
Marble
Concrete
Granite
Lightweight concrete
218
226
Ra (Bq/kg)
13-107
33-61
7-140
25-193
1-67
1-63
18-67
ND-160
10-60
232
Th (Bq/kg)
7- 62
45-66
8-127
29-66
0.5-190
0.4-142
3-43
ND-354
6-66
40
K (Bq/kg)
48-564
476-788
227-1140
320-1049
22-804
9-986
16-1100
24-2355
51-870
include radioactive decay chains headed by 238U, 235U, and
Th, as well as 40K, 87Rb, and other radioactive isotopes.
235
U is present in such small amounts (0.7%) compared
to 238U (99.3%) that it contributes a relatively very minor
radiation dose and therefore is not considered further.
Many scientists and researchers in the world worked in the
field of analyzing soil and rock samples to show the natural
radioactivity levels and associated radiological hazards
in the environment by using gamma‑rays spectroscopy
system since most soil and rock samples contain naturally
occurring radioactive elements. The members of two
natural radioactive series, which can be represented by the
isotopes 238U, 232Th, and primordial radionuclide 40K, are
the most important radioisotopes. The presence of these
radioisotopes in the rocks and soils causes external and
internal exposure to the people. 226Ra (238U series) can also
enhance the concentration of 222Rn and of its daughters
in the house.
232
The study of radioactivity levels and dose rate in
environmental rock samples from Taiz, Yemen, was
implemented.[18] The results showed that the mean activity
concentrations of 226Ra, 232Th, and 40K were found to be
65.58 ± 1.38, 82.93 ± 0.93, and 976.40 ± 6.11 Bq/kg,
respectively. These values exceed the maximum international
reference values (UNSCEAR, 2000) of 35, 30, and 400 Bq/
kg, respectively.[5] In addition, an X‑ray analysis showed that
there are considerable concentrations of heavy metals such
as Fe, Al, Zr, and Ti.
The natural radioactivity and radiation hazards in soil
samples collected from some areas of Himachal Pradesh,
India, were measured using gamma‑ray spectrometry. The
results of the activity concentrations of 226Ra and 232Th in
soil samples collected from these regions are higher and
40
K is lower than the world average value. The external
exposure dose has been determined from the content
of these radionuclides in soil. The study gives an annual
effective dose in the range of 0.07–0.13 mSv.[19]
The natural ionizing radiation exposure of the Spanish
population was reported.[20] The annual average effective
dose is estimated to be 1.6 mSv. Radon doses were
estimated from natural surveys carried out throughout the
country. To assess doses by ingestion, a detailed study on
consumption habit in Spain has been considered.
In Italy, a study on natural radioactivity and radon exhalation
in building materials in Italian dwellings was carried out.[21]
The study showed that several of the materials had hazard
indexes that exceeded the European Commission limit
values. Moreover, it was conforming that radon emanation
Radiation Protection and Environment | Volume 41 | Issue 4 | October-December 2018
Al-Khawlany, et al.: Review on studies in natural background radiation
from glazed tiles and basalt was lower than the radon
emanation from other materials with similar hazard indexes.
Table 3: Ranges and averages of the activity concentrations
of natural radionuclides in typical rocks and soils
The natural radionuclide levels in beach sediments collected
from the northeast coast of Tamil Nadu, India, were
determined using gamma‑ray spectrometric technique.[22]
The mean activity concentrations of 238U, 232Th, and 40K and
radiation hazard indices were calculated, and it was found
that all the values were lesser than the worldwide average
values. On the basis of lower levels of natural radioactivity,
beaches of the northeast coast of Tamil Nadu in India can
be considered as a low natural background radiation area.
Igneous rocks
Granite
Mafic
Crustal average
Salic
Sedimentary rocks
Dirty quartz
Carbonate rocks
Shale, sandstones
Arkose
Clean quartz
Beach sands
All rock (range)
Soil (average)
In Juban town in Yemen, natural and anthropogenic
radioactivity levels in soil and rock samples were assessed.[23]
The activity concentration of 226Ra, 232Th, and 40K for the
soils was 44.4 ± 4.5, 58.2 ± 5.1, and 822.7 ± 31 Bq/kg,
respectively. 137Cs was found in the investigation study
area with low‑level deposits and its activity concentrations
ranged from 0.1 ± 0.1 to 23.2 ± 1.2 Bq/kg.
Radionuclides in rock samples collected from southern
part of Nigeria have been measured using gamma‑ray
scintillation spectrometry.[24] The absorbed dose rate and
gamma radiation exposure (annual effective dose) ranged
from 0.012–0.042 to 0.06–0.21 mSv/y, respectively,
implying that the radiation from rocks is below the world
average background. The radioactivity levels depend on the
rock type. Granite rocks had the highest (882 ± 298 Bq/kg)
activity concentration of 40K because of the high silica
content and fairly high (131 ± 43 and 129 ± 38 Bq/kg)
activity concentration for 232Th and 238U, respectively.
The outdoor gamma radiation exposure dose rate
was estimated due to the activity concentration of
radionuclides 40K, 238U, and 232Th in the soil in 18 cities
across different environments in Nigeria.[25] The report
revealed 0.102 ± 0.032 µGy/h for the northern
part, 0.089 ± 0.014 µGy/h for the western part, and
0.040 ± 0.006 µGy/h for the eastern part of the country.
Table 3 shows a summary of concentrations of major
natural radionuclides in major rock types and soil in
different geological formations.[26] It can be noted that
granite and salic types have high levels of radioactivity
comparatively with other types of rocks.
The radionuclide concentration in different environmental
matrices of high‑background radiation areas of coastal
Kerala was measured.[27] The soil samples collected from
sea waterline at different depths and at different distances
were then analyzed for primordial radionuclides using
Rock type
238
U (Bq/kg)
232
Th (Bq/kg)
40
K (Bq/kg)
40
7
7-10
50
70
7
10-15
60
>1000
70-400
300
1100-1500
40
25
40
10-25
<10
40
7-60
400
10-25
8
50
<8
<8
25
7-80
37
400
70
800
600-900
<300
<300
700-1500
22
gamma‑ray spectrometry. The activity concentration of
potassium was under the detectable level in most of the
samples collected from the high‑background areas. No
definite correlation was found between the variation of
232
Th and 226Ra concentrations with depth.
The analysis of primordial radionuclides in soils from
Hassan district of South India was carried out using
NaI (Tl) detector. [28] The calibration of gamma‑ray
spectrometer was done using standard sources such as
RG‑U, RG‑Th, and RG‑K, procured from the International
Atomic Energy Agency, Vienna. The study noted that the
radionuclide concentration varied from place to place due
to the presence of different geological formations of the
region. Relatively higher activity of 232Th was observed in
this study. The Raeq was found below the recommended
limit of 370 Bq/kg. The calculated absorbed gamma dose
rate in air ranged from 49 to 116 nGy/h, with a mean value
of 71 nGy/h, and the radiological hazard parameters were
found within the safety limits.
The radon exhalation rate in sand samples collected from
the newly discovered high‑background radiation area
at Erasama beach placer deposit of Orissa, India, was
assessed.[29] Radon exhalation rates were measured by “Can”
technique using LR‑115 Type II plastic track detector to
estimate the radiation exposure in atmosphere. The sand
samples collected from Erasama beach contain the heavy
minerals.
The natural radioactivity in the sediment samples collected
from Pulicat Lake to Vada Nemmeli of Chennai coast,
East coast of Tamil Nadu, India, had been measured using
gamma‑ray spectrometry NaI (Tl) detector.[30] The study
showed that the average concentrations of 238U, 232Th, and
40
K were 10.14, 35.02, and 425.82 Bq/kg, respectively, in
sediments, which are around the world average values
Radiation Protection and Environment | Volume 41 | Issue 4 | October-December 2018
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Al-Khawlany, et al.: Review on studies in natural background radiation
(35, 30, and 400 Bq/kg, respectively) defined by the
UNSCEAR, 2000.[5] The calculated radium equivalent
activity (Raeq) of the sediment samples showed lower than
the recommended safe limit of 370 Bq/kg.
Radiological investigations recently carried out in the
Eastern coast of Odisha, India, to measure the radiation
dose rates have revealed that there is an enhanced level of
natural radiation in the area.[31] The activity concentration
of 232Th was found to be 2825 Bq/kg, whereas that of
238
U was 350 Bq/kg.
Measurement of natural radioactivity in some selected rock
samples from Dhanbad city of Jharkhand, India, was done
using gamma‑ray spectrometry.[32] The study showed that
the activity concentrations ranged from detection limit to
3.08 Bq/kg for 226Ra and 5.35−37.39 Bq/kg for 232Th and
168.8−416.9 Bq/kg for 40K. The concentrations of these
radionuclides were compared with the recommended
values. The study results showed that the Raeq due to
natural radioactivity was 51.34 Bq/kg in the rock samples,
which is very low compared to the world average of
370 Bq/kg. The average values of indoor and outdoor
annual effective dose rates (0.125 and 0.016 mSv/y,
respectively), external hazard index (Hex: 0.14), internal
hazard index (0.13), and gamma level index Iγ (0.20) were
found to be lower than the internationally acceptable values.
Hence, all the rock samples do not pose any significant
source of radiation hazard, and the use of the rock samples
in the construction of dwellings is considered to be safe
for inhabitants.
The radionuclides in soil samples collected from Hamirpur
district, Himachal Pradesh, India, were analyzed.[33] The
specific activity concentrations of natural radionuclide
226
Ra, 232Th, and 40K in the selected soil samples was
analyzed using gamma‑ray spectrometry, NaI (Tl) detector.
The gamma ray lines of 1.46, 1.76, and 2.62 MeV,
respectively, were employed for potassium, radium, and
thorium estimation.
Natural background gamma radiation levels in and around
Loktak Lake of Manipur, India, and natural pollution
level due to terrestrial gamma radiation were measured
using NaI (Tl) scintillator‑based Micro‑R‑survey meter
and high‑purity germanium detector.[34] The averaged
reported values of radioactivity concentrations of
226
Ra, 232Th, and 40K were 74.6, 112.1, and 792.9 Bq/
kg, respectively, and the average value of the annual
effective dose in this study was 0.7 ± 0.1 mSv/y, which
is higher than the world average value of about 0.4
mS/y reported by UNSCEAR, 2000.[5] The estimated
220
radionuclides (226Ra, 232Th, and 40K) were comparable
with the reported values for many countries in the world
and different places of this country.
The level of terrestrial gamma radiation and associated
dose rates from the naturally occurring radionuclides
232
Th, 238U, and 40K in ten soil samples collected from
Thanjavur (Tamil Nadu, India) were assessed using
gamma‑ray spectrometry. [35] The activity profile of
radionuclides had clearly showed the existence of
low‑level activity in Thanjavur. The average value of
activity concentrations of 232Th, 238U, and 40K was 42.9
± 9.4, 14.7 ± 1.7, and 149.5 ± 3.1 Bq/kg, respectively.
Absorbed dose rates in air outdoors were variation
between 32 and 59.1 nGy/h, with an arithmetic
mean of 43.3 ± 9 nGy/h. This value is lower than
the population‑weighed world average of 60 nGy/h.
Moreover, the annual effective dose value ranged
between 39.2 and 72.6 µSv/y with an arithmetic mean
of 53.1 ± 11 µSv/y. The values of the Hex were found
to be lower than the recommended safe levels.
The distribution of radionuclides in Indian soils had been
studied, and it has been reported that the terrestrial dose
rates range from 18 to 144 nGy/h, and the contribution of
I37
Cs toward the external dose is very small.[36] Some places
in peninsular India like Hyderabad and Visakhapatnam
and Chingleput located in the East coast exhibit higher
concentrations of 232Th compared to that of other normal
areas of India. The radioactivity level of 238U and 232Th in
soil samples from monazite regions in India varies up to
3400 and 15,400 Bq/kg, respectively.
Assessment of natural radioactivity and radiation index
parameters in sand samples collected from the coastal belt
of Kerala had been carried out using NaI (Tl) detector.[37]
This study reported that, in certain situations, the natural
radioactivity in the environmental matrices can reach
reference levels or beyond. Hence, this study had been
performed to understand the distribution and enrichment
of natural radionuclides in the coastal environment of
Kerala, thereby assessing dose to the inhabitants. The
assessment showed that the activity concentration of
226
Ra and 40K is well within the permissible limit, but the
concentration of 232Th was found higher compared to the
world and Indian average values. The sand weathered from
the rocks, which are rich in heavy metals and radioactive
minerals, can contribute to the enhanced level of 232Th
activity. In this article, the values for the indoor and outdoor
annual effective doses were of the same order as that of
world average value of 0.48 mSv.
Radiation Protection and Environment | Volume 41 | Issue 4 | October-December 2018
Al-Khawlany, et al.: Review on studies in natural background radiation
Radioactivity in foods
The concentration of radionuclides in foods is varying and
is dependent on several factors, such as the type of food and
the geographic region where the food has been produced.
Every food has some small amount of radioactivity in it.
The concentration of natural radioactivity in food is often
in the range of 40–600 Bq/kg of food. In the human
body, the concentration of activity of potassium (40K),
carbon (14C), tritium (3H), polonium (210Po), and 226Ra is
63, 66, 133, 0.0002, and 2.7 × 10−5 Bq/kg, respectively.[38]
40
K, 226Ra, and 238U and their associated progeny are the
common radionuclides found in food. In general, 40K is
the most commonly occurring natural radioisotope. For
example, levels of 40K in milk measure around 50 Bq/kg,
420 Bq/kg in milk powder, 125 Bq/kg in beef, 165 Bq/kg in
potatoes, and for bananas, meat, and other potassium‑rich
products, levels of radionuclides may measure at several
hundreds Bq/kg. Other natural radioisotopes exist in much
lower concentrations and originate from the decay of
uranium and thorium.[38] Table 4 summarizes the amount
of natural radioactivity of some common foods.[39]
Children and adults receive annual doses of 185 and
165 µSv, respectively, from 40K naturally present in their
bodies. The higher dose received by children is due to a
higher potassium concentration in the diet in relation to
body mass.[12] Moreover, the representative average annual
individual dose of 175 µSv has been determined to this
exposure pathway. Cosmic rays produce neutrons which
interact with nitrogen in the upper atmosphere to produce
carbon‑14. About 9 kg approximately of carbon‑14 is
produced in this way every year. This 14C is distributed
throughout the environment worldwide and, because
carbon is a key component of living material, carbon‑14
is present in trees and plants and therefore also in the
food chain.[40] Foods high in fatty acids are normally high
in carbon. These include oils, milk products, avocados,
almonds, walnuts, and fish such as mackerel, trout,
and salmon. Cereals also tend to have high carbon‑14
concentrations. UNSCEAR, 2000,[5] has estimated that
the worldwide average per caput dose from carbon‑14 in
the diet from nuclear weapons’ testing is 1.7 µSv. While
Table 4: Natural radioactivity of some common foods
Food
White potatoes
Red meat
Banana
Beer
Drinking water
Carrot
Raw Lima bean
Brazil nuts
40
K (Bq/kg)
125.8
111
130.24
14.43
125.8
171.68
207.2
226
Ra (Bq/kg)
0.037-0.093
0.0185
0.037
0-0.006
0.022-0.074
0.074-0.185
37-259
this value is now somewhat dated, the long half‑life of
carbon‑14 along with its behavior in the environment
means that this is a reasonably accurate estimate of the
current exposure levels.
CONCLUSIONS
Humans are always exposed to a spread of radionuclides
present in the air, water, soil, rock, food, and building
materials. The concentration of radionuclides in soils
is an indicator of radioactive accumulation in the
environment, which affects humans, animals, and plants.
These radionuclides have long life, with half‑lives often
about hundreds of millions of years. Exposures to
natural sources are due to (a) cosmic rays, (b) source of
terrestrial origin, (c) indoor inhalation exposures due to
222
Rn and their daughters, and (d) internal exposure from
radionuclides taken into the body through the ingestion
of food materials, etc., Exposures depend on the location,
elevated levels of NORMs in specific localized regions,
and human activities and practices. Especially, building
materials of houses and the design and ventilation systems
strongly influence the indoor levels of radon and its decay
products, which contribute the doses through inhalation.
The global value of total contribution from the natural
sources to the population works is 2.4 mSv/y.[10] Most of
the exposures are produced by the radioactivity of the
natural radionuclides present in the environment.
Acknowledgments
The authors would like to thank the editor and reviewers
of the Journal of Radiation Protection and Environment
(RPE) for their careful reading of our manuscript and their
useful comments and suggestions.
Financial support and sponsorship
Nil.
Conflicts of interest
There are no conflicts of interest.
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