Table 1 Committed effective ingestion dose estimates for adult residents in the Tohoku Region (µSv per annual seafood intake)

From: Ingestion doses from radionuclides in seafood before and after the Fukushima Daiichi Nuclear Power Plant accident

Radionuclides

Before the accident

0−1 yr

1–3 yrs

3−10 yrs

After the accident

90Sr, 110mAg, 131I, 134Cs, 137Cs, 239,240Pu

95th%a

3.4

19

5.1

1.9e

AMb

0.96

5.8

2.1

0.83

50th%c

0.74

3.3

1.6

0.62

5th%d

0.25

0.68

0.54

0.28

134Cs, 137Cs

95th%

2.0

15

4.3

1.3

AM

0.58

4.3

1.8

0.65

50th%

0.51

2.4

1.5

0.56

5th%

0.23

0.48

0.53

0.26

All (includes natural radionuclides)

95th%

1129

1142

1128

1125

AM

465

469

465

464

50th%

347

349

348

347

5th%

147

148

147

147

  1. a95th%: 95th percentile.
  2. bAM: arithmetic mean.
  3. c50th%: 50th percentile.
  4. d5th%: 5th percentile.
  5. eThe 95th% value for 3–10 years after the accident is not significantly different from the pre-accident value. The slightly lower apparent value reflects uncertainties in the data, particularly in the upper tail of the distributions, as well as slight decreases in ambient radionuclide concentrations over time due to radioactive decay and dispersion. Results for all radionuclides are shown at the µSv level to indicate computational differences only for comparison with results for other radionuclides. In Fig. 3, these values are rounded to avoid implying undue precision.
  6. Results for the pre-accident period, 1–3 years after the accident, and 3−10 years after the accident are presented as averaged annual doses in Phases I, V, and VI, respectively. The result for the first year after the accident is presented as the sum of doses in Phases II, III, and IV.
  7. The doses from 90Sr, 110mAg, 131I, 134Cs, 137Cs, and 239,240Pu before the accident originate from past atmospheric weapons test fallout or other nonspecific sources.