2012Journal of Environmental ProtectionOpen access

Assessment of Radioactivity Contents and Associated Risks in Some Soil Used for Agriculture and Building Materials in Cameroon

P. Tchokossa, Thomas B. Makon, Robert Martin Nemba

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Abstract

A survey of radioactivity content and associated radiological risks was carried out in various soils used for agriculture and building materials in Cameroon by means of a well-calibrated high-purity germanium detector. Soil samples were collected directly from the agricultural farms and the brick’s factories, air-dried at room temperature to a constant mass, crushed, sieved and sealed for at least one month before analysis. The specific activity of 238U ranged from 5.36 ± 0.39 to 51.28 ± 9.67 Bq﹒kg–1 with an average of 34.52 ± 7.18 Bq﹒kg–1; 232Th from 4.03 ± 1.03 to 24.74 ± 3.10 Bq﹒kg–1 with an average of 16.67 ± 4.28 Bq﹒kg–1; 40K ranged from 16.18 ± 3.11 to 467.40 ± 50.80 Bq﹒kg–1 with an average of 186.96 ± 16.21 Bq﹒kg–1; while that of the fallout 137Cs ranged from 0.00 to 4.79 ± 1.75 Bq﹒kg–1with an average of 2.32 ± 0.99 Bq kg–1; The mean result obtained for the Representative levels index (Iγ), the radium equivalent (Raeq), the total absorbed dose rate (ADR), the external hazard index (Hex), the internal hazard index (Hin) and the Ceasium intervention levels were 0.52, 72.75 Bq﹒kg–1, 33.73 nGy﹒h–1, 0.20 Bq﹒kg–1, 0.29 Bq﹒kg–1 and 0.0028 Bq﹒cm2 respectively. The discrepancies of our data can be attributed to several factors such as past nuclear disasters, geological formation, transport process, etc. Although our results are just some fractions of the international standard limit, but still within the same ranges when compared with those obtained elsewhere. This results also will serve as a baseline data for future investigations.

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A survey of radioactivity content and associated radiological risks was carried out in various soils used for agriculture and building materials in Cameroon by means of a well-calibrated high-purity germanium detector. Soil samples were collected directly from the agricultural farms and the brick’s factories, air-dried at room temperature to a constant mass, crushed, sieved and sealed for at least one month before analysis. The specific activity of 238U ranged from 5.36 ± 0.39 to 51.28 ± 9.67 Bq﹒kg–1 with an average of 34.52 ± 7.18 Bq﹒kg–1; 232Th from 4.03 ± 1.03 to 24.74 ± 3.10 Bq﹒kg–1 with an average of 16.67 ± 4.28 Bq﹒kg–1; 40K ranged from 16.18 ± 3.11 to 467.40 ± 50.80 Bq﹒kg–1 with an average of 186.96 ± 16.21 Bq﹒kg–1; while that of the fallout 137Cs ranged from 0.00 to 4.79 ± 1.75 Bq﹒kg–1with an average of 2.32 ± 0.99 Bq kg–1; The mean result obtained for the Representative levels index (Iγ), the radium equivalent (Raeq), the total absorbed dose rate (ADR), the external hazard index (Hex), the internal hazard index (Hin) and the Ceasium intervention levels were 0.52, 72.75 Bq﹒kg–1, 33.73 nGy﹒h–1, 0.20 Bq﹒kg–1, 0.29 Bq﹒kg–1 and 0.0028 Bq﹒cm2 respectively. The discrepancies of our data can be attributed to several factors such as past nuclear disasters, geological formation, transport process, etc. Although our results are just some fractions of the international standard limit, but still within the same ranges when compared with those obtained elsewhere. This results also will serve as a baseline data for future investigations.

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Available abstract

A survey of radioactivity content and associated radiological risks was carried out in various soils used for agriculture and building materials in Cameroon by means of a well-calibrated high-purity germanium detector. Soil samples were collected directly from the agricultural farms and the brick’s factories, air-dried at room temperature to a constant mass, crushed, sieved and sealed for at least one month before analysis. The specific activity of 238U ranged from 5.36 ± 0.39 to 51.28 ± 9.67 Bq﹒kg–1 with an average of 34.52 ± 7.18 Bq﹒kg–1; 232Th from 4.03 ± 1.03 to 24.74 ± 3.10 Bq﹒kg–1 with an average of 16.67 ± 4.28 Bq﹒kg–1; 40K ranged from 16.18 ± 3.11 to 467.40 ± 50.80 Bq﹒kg–1 with an average of 186.96 ± 16.21 Bq﹒kg–1; while that of the fallout 137Cs ranged from 0.00 to 4.79 ± 1.75 Bq﹒kg–1with an average of 2.32 ± 0.99 Bq kg–1; The mean result obtained for the Representative levels index (Iγ), the radium equivalent (Raeq), the total absorbed dose rate (ADR), the external hazard index (Hex), the internal hazard index (Hin) and the Ceasium intervention levels were 0.52, 72.75 Bq﹒kg–1, 33.73 nGy﹒h–1, 0.20 Bq﹒kg–1, 0.29 Bq﹒kg–1 and 0.0028 Bq﹒cm2 respectively. The discrepancies of our data can be attributed to several factors such as past nuclear disasters, geological formation, transport process, etc. Although our results are just some fractions of the international standard limit, but still within the same ranges when compared with those obtained elsewhere. This results also will serve as a baseline data for future investigations.

Key concepts: Radium, Environmental science, Soil test, Animal science, Effective dose (radiation), Radionuclide, Soil water, Environmental chemistry

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