-
From 2012 to 2019, a total of 6,129 food samples were collected and measured. Table 1 lists the mean values of radionuclides in different types of foods during the period of 2012–2019. Among all types of foods, tea had the highest mean concentrations of 238U and 228Ra at 2.88 Bq/kg and 1.75 Bq/kg, respectively, milk and dairy products were found with the highest mean concentrations of 226Ra and 137Cs at 1.13 Bq/kg and 0.79 Bq/kg, respectively, and seaweed had the highest concentration of 40K at 371 Bq/kg.
Food No. of samples 238U
mean (95%CI)228Ra
mean (95%CI)226Ra
mean (95%CI)40K
mean (95%CI)137Cs
mean (95%CI)Milk and dairy products 646 2.15 (1.95−2.35) 0.57 (0.51−0.63) 1.13 (1.00−1.26) 228.00 (218.90−237.10) 0.79 (0.64−0.94) Vegetables 2,203 0.55 (0.51−0.59) 0.29 (0.27−0.31) 0.39 (0.29−0.49) 102.00 (98.30−105.70) 0.08 (0.07−0.09) Tea 430 2.88 (2.49−3.27) 1.75 (1.52−1.98) 1.09 (0.98−1.20) 305.00 (282.60−327.40) 0.33 (0.29−0.37) Cereal 1,264 1.76 (1.63−1.89) 0.50 (0.46−0.54) 0.62 (0.57−0.67) 105.00 (98.00−112.00) 0.20 (0.17−0.23) Livestock and poultry meat 653 0.94 (0.77−1.11) 0.43 (0.36−0.50) 0.46 (0.40−0.52) 96.90 (82.63−111.17) 0.23 (0.18−0.28) Fish and seafood 802 0.95 (0.84−1.06) 0.94 (0.82−1.06) 0.55 (0.47−0.63) 67.50 (63.97−71.03) 0.04 (0.037−0.042) Seaweed 131 2.47 (1.56−3.38) 1.11 (0.90−1.32) 0.56 (0.44−0.68) 371.00 (265.68−476.32) 0.03 (0.027−0.033) Table 1. Mean concentration (Bq/kg, wet weight) of radionuclides in different foods of China, 2012−2019.
Table 2 shows the mean activity concentrations of different radionuclides in samples around the nuclear power plants during 2012–2019. Among the samples, the mean activity concentrations of 238U and 40K in seaweed were the highest, the mean activity concentrations of 228Ra and 226Ra in tea were the highest, and high activity concentration of 137Cs was found both in milk and tea.
Food No. of samples 238U
mean (95%CI)228Ra
mean (95%CI)226Ra
mean (95%CI)40K
mean (95%CI)137Cs
mean (95%CI)Milk and dairy products 202 1.09 (0.91−1.27) 0.30 (0.27−0.33) 1.20 (0.78−1.62) 185.00 (169.00−201.00) 0.32 (0.27−0.37) Vegetables 1,023 0.34(0.31−0.37) 0.31 (0.28−0.34) 0.23 (0.20−0.26) 99.80 (96.24−103.36) 0.05 (0.04−0.06) Tea 90 2.07(1.50−2.64) 2.67 (1.98−3.36) 1.51 (1.19−1.83) 335.00 (282.11−387.89) 0.32 (0.25−0.39) Cereal 336 0.95(0.85−1.05) 0.60 (0.50−0.70) 0.40 (0.36−0.44) 92.90 (81.78−104.02) 0.09 (0.08−0.10) Livestock and poultry meat 369 0.63 (0.42−0.84) 0.31 (0.24−0.38) 0.34 (0.25−0.43) 68.30 (64.75−71.85) 0.06 (0.04−0.08) Fish and seafood 768 0.96 (0.85−1.07) 0.95 (0.82−1.08) 0.55 (0.47−0.63) 67.50(63.85−71.15) 0.04 (0.038−0.042) Seaweed 109 2.49 (1.47−3.51) 1.07 (0.84−1.30) 0.57 (0.43−0.71) 382.00 (257.90−506.09) 0.03 (0.026−0.034) Table 2. Mean concentration (Bq/kg, wet weight) of radionuclides around nuclear power plants in China, 2012−2019.
Table 3 shows the mean activity concentrations in samples around the uranium mines during 2012–2019. The mean activity concentrations of 238U, 40K, and 226Ra in tea were the highest, the mean activity concentration of 228Ra in seaweed was the highest, and the mean activity concentration of 137Cs in milk and dairy products was the highest.
Food No. of samples 238U
mean (95%CI)228Ra
mean (95%CI)226Ra
mean (95%CI)40K
mean (95%CI)137Cs
mean (95%CI)Milk and dairy products 250 2.99 (2.60−3.38) 0.55 (0.49−0.61) 1.22 (1.00−1.44) 268.00 (253.74−282.26) 1.18 (0.87−1.49) Vegetables 590 0.99 (0.86−1.12) 0.25 (0.22−0.28) 0.76 (0.39−1.13) 94.60 (85.08−104.12) 0.17 (0.13−0.21) Tea 156 4.18 (3.37−4.99) 2.22 (1.80−2.64) 1.30 (1.10−1.50) 405.00 (369.38−440.62) 0.46 (0.38−0.54) Cereal 447 1.88 (1.62−2.14) 0.45 (0.39−0.51) 0.70 (0.60−0.80) 143.00 (126.68−159.32) 0.40 (0.33−0.47) Livestock and poultry meat 280 1.39 (1.09−1.67) 0.65 (0.50−0.80) 0.60 (0.53−0.67) 137.00 (104.09−169.91) 0.47 (0.36−0.58) Fish and seafood 27 0.58 (0.38−0.78) 0.65 (0.30−1.00) 0.58 (0.36−0.80) 71.40 (59.00−83.81) 0.05 (0.04−0.06) Seaweed 2 1.91 2.38 (1.26−3.50) 0.78 (0.41−1.15) 15.0 − Note: “–” means not detected. Table 3. Mean concentration (Bq/kg, wet weight) of radionuclides around the uranium mines in China, 2012−2019.
In 2 independent sample t-tests that were performed on data in Tables 2–3, differences in the radionuclide contents of fish and seafood were found between the two regions that were not statistically significant (α=0.05), and the content of 226Ra in milk and dairy products, 40K in vegetables, and 226Ra and 228Ra in tea between the two regions were also not statistically significant (α=0.05). However, the differences of radionuclides in the remaining foods between the 2 regions were statistically significant (α=0.05).
HTML
Citation: |