Abstract:
Cancer has become a major cause of mortality in the recent times. Up to 10% of invasive cancers
are related to ionizing radiation exposure, which is known to be capable of causing increase in
future incidence of cancer cases. Up till now, database on radioactivity from Africa, and Nigeria
especially are still very sparse compared to information from several other environments of North
America, Europe and Asia. Activity concentration of natural radionuclides and artificial
radiocaesium together with heavy metals concentration and soil-to-plant transfer factor have been
evaluated in soil and plant samples from seventeen states in Southern Nigeria. The samples were
analysed for radioactivity using the co-axial type Hyper-Pure Germanium (HPGe) detector
(CANBERRA, USA), while heavy metals analyses were performed using Atomic Absorption
Spectrometer (AAS). The activity concentration of 40K, 226Ra, 232Th and 137Cs in the soils ranges
from 13.06 to 2723.22 Bq kg-1, 8.53 to 160.37 Bq kg-1, 11.09 to 295.24 Bq kg-1 and 0.53 to 3.53
Bq kg-1 with the mean value of 276.40, 37.30, 56.58 and 1.26 Bq kg-1 respectively. The activity
concentration of 40K, 226Ra, 232Th and 137Cs in plants ranges from 419.79 to 9221.05 Bq kg-1, 3.67
to 56.40 Bq kg-1, 1.77 to 64.88 Bq kg-1 and 0.53 to 3.53 Bq kg-1 with a mean values of 2536.33,
19.36, 22.00 and 1.64 Bq kg-1 respectively. The radium equivalent concentration, the external and
internal hazard indices were estimated to range from 28.47 to 701.53 Bq kg-1, 0.08 to 1.89 and
0.10 to 2.33 with mean values of 139.50 Bq kg-1, 0.38 and 0.48 respectively. The mean values of
Zn, Cd, Mn, Co, Ni and Pb concentrations in the soils were 82.70, 0.07, 183.98, 2.81, 5.71, and
27.67 mg kg-1 respectively. The mean values of Zn, Cd, Mn, Co, Ni and Pb concentrations in the
plants were found to be 225.31, 0.49, 198.36, 2.06, 7.63, and 7.59 mg kg-1, respectively. The mean
daily intake of heavy metals through vegetable consumption in the study areas was estimated at
80.25, 0.18, 70.65, 0.73, 2.72 and 2.70 mg d-1 for Zn, Cd, MN, Co, Ni and Pb respectively. The
mean absorbed dose and the annual outdoor effective dose in soil samples were higher in the South-
West (95.40 nGy h-1 and 0.12 mSv y-1) than in the South-South (32.30 nGyh-1 and 0.04 mSv y-1)
and South-East (45.53 nGy h-1 and 0.06 mSv y-1), the world average (0.07 mSv y-1) and
international permissible standards of 0.1 mSv y-1 and 1.0 mSv y-1 for World Health Organization
(WHO) and International Commission on Radiological Protection (ICRP) respectively. The soilto-
plant transfer factor estimation showed that 40K has very high value compared to other
radionuclides in the samples. Regression analysis showed that there was no linearity (R ranges
from -0.83 to -0.34) in the relationship between activity concentration of radionuclides in soils and
in plants because plant receives some amount of radionuclide concentration from other sources
like air, rainwater, and cosmic rays. The mean daily intake of heavy metal was higher than the
values from literatures and recommended limit by International Atomic Energy Agency (IAEA)
and ICRP. There were some degree of linearity in the relationship between the activity
concentration of radionuclides and concentration of heavy metals in the soil with few cases of
weak or insignificant correlation (R ranges from -0.24 to 0.50). This could be because
radionuclides and heavy metals have different origin. The mean probability of developing cancer
in a lifetime by inhabitants of the study areas through residential soil channels and vegetables is
5.55 x 10-5 and 1.94 x 10-3 respectively. This implied that from every one million humans, 56 and
1,940 persons respectively for residential soil and vegetable consumption pathways, are liable to
developing cancer during a life time. This value constitutes an important fraction of the 1% of
global population that was estimated by Biological Effect of Ionizing Radiation (BEIR) report of
developing cancer as a result of natural background radiation at some points in their lifetime.