Open Access
Article

Journal of Radioanalytical and Nuclear Chemistry

, Volume 295, Issue 2, pp 1245-1249

A preliminary study on 226Ra, 232Th, 40K and 137Cs activity concentrations in vegetables and fruits frequently consumed by inhabitants of Elazığ Region, Turkey

Authors

  • Cumhur Canbazoğlu
    • Department of Physics, Faculty of Arts and SciencesKilis 7 Aralık University
  • Mahmut Doğru
    • Department of Physics, Faculty of Arts and SciencesBitlis Eren University

DOI: 10.1007/s10967-012-1995-4

Abstract

Determining radioactivity levels in foodstuffs is of great importance for the protection of human health. In addition, the literature includes few studies related to this subject in Turkey. In this study, gamma spectroscopic system was used in order to measure 226Ra, 232Th, 40K and 137Cs activity concentrations in vegetables and fruits produced in Elazığ Region. The average activity concentrations in vegetables was calculated as 0.64 ± 0.26 Bq kg−1 for 226Ra, 0.65 ± 0.14 Bq kg−1 for 232Th, 13.98 ± 1.22 Bq kg−1 for 40K, and 0.54 ± 0.04 Bq kg−1 for 137Cs. The average activity concentrations in fruits were 1.52 ± 0.34, 0.98 ± 0.23, 18.66 ± 1.13 and 0.59 ± 0.16 Bq kg−1, respectively for 226Ra, 232Th, 40K and 137Cs. Total committed effective dose value was determined as 20 and 30.55 μSv y−1, respectively for vegetables and fruits. The findings were compared with previous data reported for Turkey and other regions of the world.

Keywords

Effective dose Food stuff Internal dose Elazığ

Introduction

Natural radionuclide concentrations in environmental samples varies according to geographical and geological factors [1]. Natural sources of radioactivity in the environment are called naturally occurring radioactive materials, and are categorized as being of terrestrial or cosmic origin [2]. Humans are exposed to both internal and external radiation from these natural sources. Internal exposure occurs through the intake of terrestrial radionuclides through inhalation or ingestion. Inhalation exposure dose results from the existence of dust particles in air, including radionuclides from 238U and 232Th decay series. The biggest contribution to inhalation exposure comes from short half-life decay products of radon. Ingestion exposure dose mostly results from 238U and 232Th series radionuclides and 40K in drinking water and foodstuff. In addition, 137Cs is the most important fission product released to the environment as a result of nuclear activities, because this radionuclide rapidly passes to foodstuffs and creates a dose effect [3]. The literature includes this type of studies [410]. The aim of this study is to determine the exposure dose of 226Ra, 232Th, 40K and 137Cs radionuclide concentrations in fruits and vegetables produced in the Elazığ Region of Turkey, which are frequently consumed by local residents. The significance of the study is that it is the first study to determine the background radiation levels in such food products in this region and will provide data for future studies and in case of a nuclear accident (as in Chernobyl nuclear accident) or nuclear fallout, to determine level of contamination.

The province of Elazığ is located in the Eastern Anatolian Region, between longitude 38°30′–40°21′E and latitude 38°17′–39°11′N. Its surface area is 9,151 km2 and the average altitude is 1,067 m. The region is divided into 11 administrative regions, with a total population of 540,000 (Fig. 1). Approximately 50 % of the province consists of grasslands, 28 % is agricultural land, 12 % forest, and 10 % is dams and lakes. A continental climate prevails; winters are cold and snowy, and summers are hot and arid. The province is rich in mineral resources, and mining activities include copper, fluoride, chalcopyrite, zinc, lead, chrome, manganese, molybdenum, iron and wolfram [11].
https://static-content.springer.com/image/art%3A10.1007%2Fs10967-012-1995-4/MediaObjects/10967_2012_1995_Fig1_HTML.gif
Fig. 1

Map of Turkey showing the study area

Materials and methods

Radioactivity measurements in vegetable and fruit samples

Samples of fruits and vegetables produced and frequently consumed in the region were provided from a public market. Any soil or foreign materials on the samples were removed so that they were suitable for consumption, divided into small pieces, and washed under distilled water. They were kept at room temperature for 3 months without allowing any contamination and then totally oven-dried at 105 °C. Afterwards, incineration was applied, which was realized through dry ashing. The temperature of the oven was increased to 250 °C and was continued until the samples were reduced to ash. The ashed samples were then homogenized and transferred into a plastic container (5 cm height × 5 cm diameter). Finally, the samples were sealed and stored for a period of about 1 month before counting, in order to allow equilibrium between 226Ra and its short-lived decay products.

The activity concentrations of 226Ra, 232Th, 40K and 137Cs radionuclides in vegetable and fruit samples were determined using a gamma spectroscopic system, comprising a 2″ × 2″ NaI(Tl) well-type detector and a detector surrounded by a cylindrical lead shield (thickness, diameter and length approximately 3.5, 13.7 and 15.5 cm, respectively). The detector window was made of aluminum of 0.50 mm thickness. Energy calibration of detector was performed by using 60Co (37 kBq) and 226Ra (370 kBq) point sources. Photopeak efficiency was 24 %. 226Ra, 232Th, 40K and 137Cs activity concentrations in vegetable and fruit were based on the detection of 609.3, 583, 1461 and 662 keV energy gamma rays transmitted by 214Bi, 208Tl, 40K and 137Cs, respectively.

Calculation of activity concentration in vegetable and fruits

The activity concentrations in vegetable and fruit samples were calculated using Eq. (1)
$$A({\rm{Bq}}\,{\rm{kg}}^{{ - 1}} ) = \frac{C}{{M_{{\rm{s}}} \varepsilon P_{\gamma } }}$$
(1)
where C is the gamma ray count (number per second), ε is the detector efficiency of the specific gamma ray, P γ is the absolute transition probability of gamma decay and M s is the mass of the sample (kg) [12].

Dose estimation

Ingestion dose occurring through the intake of radionuclides depends on the consumption rate of foodstuff and the concentration of the radionuclide involved. Ingestion dose is calculated with the Eq. (2) [3, 13, 14]
$$ H_{\text{T,r}} = \mathop \sum \nolimits \left( {U^{i} C_{\rm{r}}^{i} } \right)g_{\text{T,r}} $$
(2)
where i is foodstuff group, \( U^{\it i} \) and \(C_{\rm{r}}^{i} \) are annual consumption rate (kg) and radionuclide activity concentration (Bq kg−1), respectively for their coefficients, and \( g_{\text{T,r}} \) is dose conversion coefficient for r radionuclide (Sv Bq−1). Dose conversion coefficients of 226Ra, 232Th, 40K and 137Cs radionuclides for the adult members of society are 4.5 × 10−8, 2.3 × 10−7, 6.2 × 10−9 and 1.3 × 10−8 Sv Bq−1, respectively [13, 15, 16].

Results and discussion

Table 1 shows the natural and manmade radionuclide activity concentrations measured in samples of vegetables and fruits frequently consumed in Elazığ and its surrounding region. Minimum detectable activity values for vegetable and fruit samples were calculated as 0.02 Bq for 232Th and 137Cs; 0.03 Bq for 226Ra; and 0.1 Bq for 40K. Average activity concentrations of 226Ra, 232Th, 40K and 137Cs of vegetable samples were 0.64 Bq kg−1 (SD: 0.26), 0.65 Bq kg−1 (SD: 0.14), 13.98 Bq kg−1 (SD: 1.22) and 0.54 Bq kg−1 (SD: 0.04), respectively. The activity concentrations ranged between 0.11 and 0.99 Bq kg−1 for 226Ra; 0.47–0.84 Bq kg−1 for 232Th; 2.14–44.77 Bq kg−1 for 40K; and 0.17–0.79 Bq kg−1 for 137Cs. Average concentrations of 226Ra for fruits were 1.52 Bq kg−1 (SD: 0.34) and the values ranged between 0.73 and 2.81 Bq kg−1. 232Th concentrations ranged between 0.26 and 1.96 Bq kg−1 (average 0.98 Bq kg1, SD: 0.23). The average activities of 40K and 137Cs radionuclides were 18.66 Bq kg−1 (SD: 1.13) and 0.59 Bq kg−1 (SD: 0.16), respectively. 40K concentrations ranged between 1.34 and 35.49 Bq kg−1.
Table 1

Activity concentrations of vegetables and fruits

ID

Species

Scientific name

Activity concentrations of vegetables and fruits (Bq kg−1fresh weight)

226Ra

232Th

40K

137Cs

Vegetables

 F1

Bell pepper

Capsicum annuum L.

BDL

BDL

7.21 ± 0.91

0.48 ± 0.04

 F2

Parsley

Petroselinum crispum

(Mill.) Nyman & A.W. Hill

BDL

BDL

44.77 ± 1.90

BDL

 F3

Scallion

Allium cepa L.

BDL

0.84 ± 0.17

29.41 ± 1.85

BDL

 F4

Pumpkin

Cucurbita moschata Duchesne ex Poir.

BDL

BDL

2.14 ± 1.36

BDL

 F5

Leek

Allium ampeloprasum

0.64 ± 0.37

BDL

10.02 ± 1.15

BDL

 F6

Radish

Raphanus sativus L.

0.11 ± 0.04

0.47 ± 0.05

3.43 ± 0.34

0.17 ± 0.01

 F7

Kale

Brassica oleracea Acephala

BDL

0.64 ± 0.24

5.78 ± 1.57

BDL

 F8

Capsicum

Capsicum annuum L.

BDL

BDL

5.78 ± 0.63

BDL

 F9

Cabbage

Brassica oleracea Capitata

0.95 ± 0.09

BDL

26.95 ± 0.95

BDL

 F10

Tomato

Solanum lycopersicum L.

0.45 ± 0.08

0.64 ± 0.09

10.73 ± 0.70

BDL

 F11

Eggplant

Solanum melongena L.

0.99 ± 0.19

BDL

16.57 ± 1.60

0.79 ± 0.06

 F12

Lettuce

Lactuca sativa L.

BDL

BDL

30.93 ± 1.41

0.72 ± 0.05

 F13

Spinach

Spinacia oleracea L.

0.80 ± 0.33

BDL

9.84 ± 0.92

BDL

 F14

Peppermint

Mentha spicata L.

0.60 ± 0.36

BDL

2.22 ± 1.05

BDL

 F15

Garden Cress

Lepidium sativum L.

0.54 ± 0.61

BDL

3.97 ± 1.90

BDL

Average

0.64 ± 0.26

0.65 ± 0.14

13.98 ± 1.22

0.54 ± 0.04

Fruits

 F16

Melon

Cucumis melo L.

1.01 ± 0.13

0.48 ± 0.13

35.49 ± 0.99

0.53 ± 0.04

 F17

Pear

Pyrus spp.

BDL

1.96 ± 0.33

13.62 ± 1.60

BDL

 F18

Quince

Cydonia oblonga Mill.

2.81 ± 0.45

1.14 ± 0.31

23.01 ± 1.40

0.64 ± 0.27

 F19

Grapes

Vitis vinifera L.

BDL

0.26 ± 0.12

1.34 ± 0.63

BDL

 F20

Watermelon

Citrullus lanatus (Thunb.) Matsum & Nakai

BDL

BDL

34.44 ± 0.88

BDL

 F21

Apple

Malus domestica Borkh.

0.73 ± 0.45

1.04 ± 0.26

4.04 ± 1.25

BDL

Average

1.52 ± 0.34

0.98 ± 0.23

18.66 ± 1.13

0.59 ± 0.16

BDL below detection limit

Effective dose values exposed due to radionuclides taken into body through the consumption of fruit and vegetable samples are shown in Table 2. Primarily, average activity concentration (Bq kg−1) for each radionuclide was multiplied by food consumption rate, and annual activity intake value was determined in Bq unit. Food consumption rate was taken as 73 kg a−1 for both fruits and vegetables. This value represents the average consumption for Turkey [17]. The effective dose value was then determined by multiplying annual activity intake value by effective dose coefficient. Effective dose values of fruit samples for all radionuclides (226Ra, 232Th, 40K and 137Cs) were higher than those for vegetable samples. Average effective exposure dose through the consumption of vegetable samples were 2.12 μSv y−1 (SD: 0.86), 11.04 μSv y−1 (SD: 2.3), 6.33 μSv y−1 (SD: 0.55) and 0.51 μSv y−1 (SD: 0.04), respectively for 226Ra, 232Th, 40K and 137Cs. Effective dose values of 226Ra, 232Th, 40K and 137Cs ranged between 0.36 and 3.25, 7.89 and 14.10, 0.97 and 20.26 and 0.16 and 0.75 μSv y−1, respectively. Average effective doses through the consumption of fruit samples were 4.99 μSv y−1 (SD: 1.13), 16.56 μSv y−1 (SD: 3.91), 8.44 μSv y−1 (SD: 0.52) and 0.56 μSv y−1 (SD: 0.16), respectively for 226Ra, 232Th, 40K and 137Cs. Dose values ranged between 2.40 and 9.23 μSv y−1 for 226Ra; 4.37 and 32.91 μSv y−1 for 232Th; and 0.61–16.06 μSv y−1 for 40K.
Table 2

Dose coefficients and committed effective dose values for 226Ra, 232Th, 40K and 137Cs

Radioisotopes

Activity intake (Bq)

Effective dose coefficient (μSv Bq−1)

Committed effective dose (μSv y−1)

Range

Average

Vegetables

 226Ra

47 ± 19

0.045

0.36 ± 0.13–3.25 ± 0.62

2.12 ± 0.86

 232Th

48 ± 10

0.23

7.89 ± 0.84–14.10 ± 2.85

11.04 ± 2.3

 40K

1021 ± 89

6.2 × 10−3

0.97 ± 0.62–20.26 ± 0.86

6.33 ± 0.55

 137Cs

39 ± 3

1.3 × 10−2

0.16 ± 0.01–0.75 ± 0.06

0.51 ± 0.04

Fruits

 226Ra

111 ± 25

0.045

2.40 ± 1.48–9.23 ± 1.48

4.99 ± 1.13

 232Th

72 ± 17

0.23

4.37 ± 2.02–32.91 ± 5.54

16.56 ± 3.91

 40K

1362 ± 83

6.2 × 10−3

0.61 ± 0.29–16.06 ± 0.45

8.44 ± 0.52

 137Cs

43 ± 12

1.3 × 10−2

0.56 ± 0.16

Table 3 shows committed effective dose values reported for some countries and regions [3, 1821]. Total adult effective dose from vegetables and fruits frequently produced and consumed in Elazığ Region for 226Ra, 232Th, 40K and 137Cs radionuclides were calculated as 20 μSv y−1 (SD:3.75) and 30.55 μSv y−1 (SD:5.72), respectively. In summary, this study found that adults living in the study region intake a radiation dose of approximately 50.55 μSv y−1 from fruit and vegetable consumption. This radiation dose (50.55 μSv y−1) is lower than the world average value (290 μSv y−1) and presents no risk to public health [3]. Dose values obtained in this present study reflect other reported values in general.
Table 3

Average effective dose values for Elazığ Region and its comparison with literature

Region/country

Committed effective dose (μSv y−1)

References

Vegetables

Fruits

Foodstuff

North America

110

[3]

Asia

110

[3]

Europe

110

[3]

Korean

110

[18]

Jos Plateau/Nigeria

(0.2–2,164)

[19]

Accra metropolitan area/Ghana

4,640

[20]

Rize/Turkey

227

63

[21]

Elazığ/Turkey

20

30.55

Present study

Conclusion

226Ra, 232Th, 40K and 137Cs radionuclide concentrations in vegetables and fruits that are produced and frequently consumed in the Elazığ Region of Turkey were determined in this study. It was found that the radiation dose due to consumption of vegetables and fruits was less than the world average, and poses no threat to public health. The results were lower than the committed effective dose values reported for various regions and countries.

Acknowledgments

We thank Dr. Mehmet Emin Sönmez for his contribution to producing the maps.

Open Access

This article is distributed under the terms of the Creative Commons Attribution License which permits any use, distribution, and reproduction in any medium, provided the original author(s) and the source are credited.

Copyright information

© The Author(s) 2012