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Research Article

Unexpected source of Fukushima-derived radiocesium to the coastal ocean of Japan

Virginie Sanial, Ken O. Buesseler, Matthew A. Charette, and Seiya Nagao
PNAS October 17, 2017 114 (42) 11092-11096; first published October 2, 2017; https://doi.org/10.1073/pnas.1708659114
Virginie Sanial
aDepartment of Marine Chemistry and Geochemistry, Woods Hole Oceanographic Institution, Woods Hole, MA 02543;
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  • For correspondence: kbuesseler@whoi.edu virginie.sanial.vs@gmail.com
Ken O. Buesseler
aDepartment of Marine Chemistry and Geochemistry, Woods Hole Oceanographic Institution, Woods Hole, MA 02543;
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  • For correspondence: kbuesseler@whoi.edu virginie.sanial.vs@gmail.com
Matthew A. Charette
aDepartment of Marine Chemistry and Geochemistry, Woods Hole Oceanographic Institution, Woods Hole, MA 02543;
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Seiya Nagao
bLow Level Radioactivity Laboratory, Institute of Nature and Environmental Technology, Kanazawa University, Kanazawa 920-1192, Japan
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  1. Edited by David M. Karl, University of Hawaii, Honolulu, HI, and approved August 28, 2017 (received for review May 24, 2017)

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    Fig. 1.

    Sample locations and 137Cs activities near the Fukushima Dai-ichi Nuclear Power Plant (FDNPP). (A) Sample locations in the vicinity of the FDNPP. The seawater data (open squares) are from the Japan Atomic Energy Agency online database. The beach groundwater (GW), surf zone, and freshwater samples were collected between 2013 and 2016. (B) 137Cs activities determined in brackish groundwater underneath beaches, freshwater (irrigation wells and rivers), and seawater from the beach surf zones plotted vs. salinity. The error bars are smaller than the symbols. The lines denote the 137Cs Japanese drinking water (DW) limit, the median 137Cs activity in seawater after the FDNPP accident (excluding the FDNPP harbor), and the 137Cs activity level in seawater before the FDNPP accident.

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    Fig. S1.

    137Cs activities in seawater during the study period. 137Cs measured in seawater within the 100 km offshore from the FDNPP (excluding the harbor). The locations of the samples are shown in Fig. 1A. Because of the larger number of samples collected close to the FDNPP where the 137Cs activities were higher, we used the median rather than the average. The median of the 137Cs activity in seawater during 2013–2015 was 14 Bq⋅m−3. The median 137Cs activity determined in the FDNPP harbor was 1,900 Bq⋅m−3 in Summer 2012 (green line) and 380 Bq⋅m−3 during the period 2013–2015 (red line). Data are from the Japan Atomic Energy Agency (JAEA), database for Radioactive Substance Monitoring Data. Available at emdb.jaea.go.jp/emdb/en/. No data were published by JAEA for the year 2016; however, according to the Nuclear Regulation Authority (NRA) (Japan), the 137Cs activities remained constant between 2013 and 2016 in the surface offshore water (radioactivity.nsr.go.jp/en/contents/8000/7745/24/okiai.pdf). Similarly, no data were published by JAEA regarding the Cs harbor activity for the year 2016; however, the Tokyo Electric Power Company (TEPCO) reported relatively comparable Cs activities in the harbor between 2013 and 2016 (www.tepco.co.jp/en/nu/fukushima-np/f1/smp/indexold-e.html). Therefore, we assumed that the medians of 137Cs activities for offshore seawater and for the harbor that we estimated based on JAEA data are valid for the period 2013–2016.

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    Fig. S2.

    Vertical profiles of 137Cs activities in beach sand. The sand cores were collected on November 16, 2016, at Yostukura beach, 35 km south of the FDNPP (Fig. 1A). The error bars are smaller than the symbols (3% on average). The bulk density of each sample, estimated based on the volume and the weight of the dry sand, was used to convert the 137Cs activity from becquerels per kilogram into becquerels per cubic meter in order to estimate the inventory. The 137Cs inventory of the deepest sand core (core 4) was 4.8 ± 0.6 × 105 Bq⋅m−2 determined by integrating the Cs activity over each 5-cm layer of sand and by summing the integrated activities. The uncertainty on the sand core Cs inventory results from the propagation of the error on each Cs activity in sand samples from the core, and is a minimum estimate as we did not reach 137Cs-free sands below.

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    Fig. 2.

    Sources of Fukushima-derived radiocesium to the coastal ocean off Japan in 2013–2016. As detailed in the text, the two known ongoing sources of dissolved 137Cs include the FDNPP via flushing of its harbor (0.6 TBq⋅y−1) and river runoff (0.2–1.2 TBq⋅y−1). We report here a previously unknown source of dissolved 137Cs to the ocean from submarine groundwater discharge (SGD) along the Japan coastline of between 0.2 and 1.1 TBq⋅y−1 (average, 0.6 TBq⋅y−1). The main driving forces of submarine groundwater from beaches are waves (W), hydraulic head (H), tidal pumping (T), and convection (C). The southward flowing coastal current, represented by the light blue arrow, would have carried extremely high 137Cs, some fraction of which was sorbed onto beach sands and later released as indicated by this study.

  • Fig. S3.
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    Fig. S3.

    Tide chart and 137Cs, 223Ra, and 224Ra activities in surf zone samples collected at Yotsukura beach. The tide data are from the Onahama station (Tide Times and Tide Charts Worldwide; available at https://www.tide-forecast.com/). Seawater samples were collected from approximatively the same location at the surf zone of Yotsukura beach over a tide cycle during the November 2016 sampling trip. High Cs and Ra activities were measured at the surf zone during low tide, and lower Cs and Ra activities were measured at rising tide, demonstrating that groundwater is a source of Ra and Cs to the surf zone and the role played by the tidal pumping in the release of groundwater Cs to the ocean.

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    Fig. S4.

    Desorption fraction as a function of the salinity of the seawater solutions. Details on 137Cs activities and locations of the three sand samples used in the experiments are reported in Table S3.

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    Fig. S5.

    224Ra and 223Ra activities in groundwater including freshwater, brackish, and surf zone seawater as a function of salinity. The radium data are from all of the groundwater samples collected in 2013–2016. The uncertainties are reported on the graph. The dashed line represents the conservative mixing line between freshwater and seawater.

  • Fig. S6.
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    Fig. S6.

    Distribution of 137Cs activity in groundwater. A bootstrapping method was used to determine the statistical mean 137Cs activities in groundwater underneath sand beaches. The solid line and the dashed line represent the average and the SD of the bootstrap mean distribution, respectively. The bootstrap method was run 1,000 times on groundwater data displaying a salinity between 5 and 30 to limit the influence from estuary or seawater. The groundwater samples were collected randomly and are uniformly distributed across the salinity gradient (Fig. 1B). The distribution of 137Cs in groundwater is a combination of several factors including the 137Cs activity in beach sand, the minerology of the sand layer, and groundwater salinity. All of these vary spatially and temporally. Using a bootstrap method to calculate the statistical mean is the best approach for representing the average Cs activity.

Tables

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    Table S1.

    Activities of dissolved 137Cs and 134Cs, and of 223Ra and 224Ra, in groundwater, river, irrigation well, natural spring, and surf zone samples collected between 2013 and 2016 in the vicinity of the Fukushima Dai-ichi Nuclear Power Plant (FDNPP)

    SamplePush point sampler length, mDistance from FDNPP, kmSampling dateLat, °NLon, °ESalinity137Cs, Bq⋅m−3134Cs, Bq⋅m−3223Ra, dpm⋅100 L−1224Ra, dpm⋅100 L−1
    Groundwater
     Funatsuke2505/17/1336.955140.94433.7138 ± 3132 ± 311.5 ± 1.2188.4 ± 4.2
    25/17/1336.955140.9413.5214 ± 4203 ± 40.8 ± 0.119.6 ± 0.7
     Kawahata2405/18/1337.057140.97333.3371 ± 7351 ± 747.3 ± 4.4877.5 ± 17.2
    25/18/1337.057140.9738.4124 ± 3119 ± 36.0 ± 0.7118.0 ± 2.5
     Yotsukura2355/18/1337.105140.9920.8119 ± 2114 ± 20.18 ± 0.17.0 ± 0.4
    210/15/1437.104140.9928.014,500 ± 3005,700 ± 1002.7 ± 0.541.3 ± 1.1
    110/15/1437.104140.99210.05,200 ± 1001,690 ± 303.3 ± 0.3123.0 ± 1.9
    110/18/1537.104140.99210.7600 ± 10140 ± 35.5 ± 0.8101.3 ± 2.8
    210/18/1537.104140.99213.87,200 ± 1501,660 ± 3015.3 ± 1.6236.0 ± 5.1
    110/18/1537.104140.99222.911,400 ± 2002,640 ± 5020.1 ± 2.1277.2 ± 6.2
    111/14/1637.104140.9923.081 ± 213 ± 10.3 ± 0.116.6 ± 0.9
    111/14/1637.104140.99218.1217 ± 435 ± 15.6 ± 0.5190.5 ± 2.4
    111/14/1637.104140.9925.9158 ± 325 ± 11.4 ± 0.250.1 ± 0.8
    211/14/1637.103140.99230.4366 ± 760 ± 113.7 ± 0.7365.4 ± 3.3
    111/15/1637.103140.99233.757 ± 19 ± 113.5 ± 0.9403.9 ± 5.2
    111/15/1637.103140.99233.748 ± 18 ± 116.6 ± 0.9382.9 ± 4.0
    211/15/1637.103140.99227.5258 ± 541 ± 110.0 ± 0.7286.1 ± 3.5
    211/15/1637.104140.99218.8224 ± 537 ± 15.3 ± 0.5226.7 ± 3.3
    111/15/1637.104140.99211.492 ± 215 ± 13.4 ± 0.489.3 ± 1.6
    111/15/1637.104140.9926.6299 ± 649 ± 11.2 ± 0.261.2 ± 1.4
    111/15/1637.104140.9920.837 ± 16 ± 10.1 ± 0.12.5 ± 0.3
    211/16/1637.103140.99121.991 ± 215 ± 17.2 ± 0.5257.3 ± 2.1
    211/16/1637.103140.99120.7120 ± 220 ± 110.9 ± 0.6281.6 ± 3.0
    211/16/1637.103140.99121.242 ± 16 ± 14.6 ± 0.5186.6 ± 3.0
    211/16/1637.104140.9928.723,000 ± 4603,800 ± 802.5 ± 0.3117.5 ± 1.4
    112/1/1637.103140.99220.020 ± 13 ± 111.2 ± 1.2163.7 ± 4.6
    212/1/1637.104140.99212.8149 ± 325 ± 15.36 ± 0.6130.7 ± 3.5
    112/1/1637.104140.9922.8119 ± 219 ± 10.5 ± 0.224.5 ± 2.0
    212/2/1637.103140.99218.787 ± 214 ± 117.2 ± 1.6164.7 ± 4.3
    112/2/1637.103140.99229.532 ± 15 ± 117.7 ± 1.4295.8 ± 3.8
    112/2/1637.103140.99224.229 ± 14 ± 112.0 ± 1.1161.6 ± 2.6
    112/2/1637.103140.99229.428 ± 14 ± 110.8 ± 2.0219.6 ± 8.9
    112/2/1637.103140.99230.827 ± 14 ± 118.4 ± 1.4314.1 ± 4.0
    112/2/1637.104140.99210.457 ± 19 ± 15.3 ± 0.772.3 ± 2.5
    112/2/1637.104140.99212.1163 ± 327 ± 15.4 ± 0.686.1 ± 2.6
     Nobiru21059/16/1338.365141.16118.617 ± 114 ± 11.7 ± 0.368.1 ± 1.2
    29/16/1338.365141.1614.310 ± 111 ± 10.4 ± 0.14.3 ± 0.3
     Nagahama2909/16/1338.261141.02025.325 ± 123 ± 14.8 ± 0.9104.0 ± 2.3
    29/16/1338.261141.02029.011 ± 111 ± 15.6 ± 0.5137.0 ± 1.9
     Iwasawa12010/19/1537.241141.0130.945 ± 110 ± 10.8 ± 0.110.7 ± 0.3
    110/19/1537.241141.0137.3146 ± 335 ± 14.4 ± 0.958.6 ± 2.6
    110/19/1537.241141.01312.8368 ± 885 ± 18.3 ± 1.3106.1 ± 3.7
    110/19/1537.241141.01321.11,060 ± 20250 ± 548.4 ± 2.8560.0 ± 7.8
    110/19/1537.241141.01325.61,000 ± 20240 ± 528.3 ± 2.3399.0 ± 6.5
     Karasuzaki23010/20/1537.686141.01310.3218 ± 452 ± 12.4 ± 0.471.8 ± 1.4
    210/20/1537.686141.01314.4570 ± 10129 ± 37.4 ± 0.8156.3 ± 2.9
    210/20/1537.686141.01315.7550 ± 10126 ± 310.4 ± 1.1149.8 ± 3.1
    210/20/1537.686141.01325.62,100 ± 40489 ± 119.7 ± 1.1207.3 ± 3.8
     Nakaso16510/22/1536.864140.7908.9530 ± 10126 ± 311.7 ± 1.3251.9 ± 5.0
    210/22/1536.864140.79015.0490 ± 10111 ± 335.3 ± 2.4490.6 ± 7.1
    210/22/1536.864140.79023.0660 ± 10147 ± 450.3 ± 3.1574.1 ± 8.1
    110/14/1436.864140.79032.098 ± 232 ± 17.0 ± 0.5258.8 ± 2.6
    210/15/1436.864140.7908.0150 ± 357 ± 17.8 ± 0.6177.2 ± 2.0
    110/14/1436.864140.79027.0300 ± 6119 ± 311.1 ± 0.8228.4 ± 2.4
    Rivers
     Natsui3110/18/1537.671140.8810.10.67 ± 0.10BDL -BDL -5.23 ± 0.34
     Kido1710/19/1537.272141.0000.00.49 ± 0.06BDL -0.09 ± 0.082.73 ± 0.22
     Niido3110/20/1537.698140.9690.10.66 ± 0.09BDL -BDL -1.33 ± 0.14
     Mano2910/20/1537.668140.9320.13.08 ± 0.070.63 ± 0.080.13 ± 0.101.30 ± 0.26
     Same6610/22/1536.864140.7900.20.84 ± 0.08BDL -0.34 ± 0.193.23 ± 0.54
    Irrigation wells
     Well 15210/18/1536.960140.9480.04.03 ± 0.120.90 ± 0.072.88 ± -2.88 ± 0.22
     Well 24210/18/1537.044140.9590.15.76 ± 0.221.14 ± 0.190.38 ± 0.094.87 ± 0.23
     Well 31710/19/1537.270141.0040.10.51 ± 0.07BDL -1.25 ± 0.1635.16 ± 0.64
     Well 43510/20/1537.737140.9890.10.00 ± 0.00BDL -0.27 ± 0.140.22 ± 0.39
    Natural spring2310/20/1537.630141.0070.20.99 ± 0.12BDL -0.75 ± 0.1318.46 ± 0.37
    Surf zone
     Yotsukura3510/18/1537.104140.99232.727.4 ± 0.585.9 ± 0.21.23 ± 0.128.90 ± 0.5
     Yotsukura3511/15/1637.103140.99233.223.4 ± 0.633.0 ± 0.22.21 ± 0.374.14 ± 1.1
     Yotsukura3511/15/1637.103140.99233.814.8 ± 0.381.9 ± 0.21.08 ± 0.243.75 ± 0.7
     Yotsukura3511/15/1637.103140.99233.816.6 ± 0.372.4 ± 0.11.82 ± 0.349.44 ± 1.2
     Yotsukura3511/16/1637.104140.99233.4191.3 ± 3.9432.0 ± 0.8ND ± NDND ± ND
     Nobiru1069/16/1338.365141.16118.59.5 ± 0.228.1 ± 0.30.10 ± 0.115.90 ± 0.7
     Nagahama939/16/1338.261141.02028.545.7 ± 1.2438.4 ± 1.70.14 ± 0.11.53 ± 0.3
     Iwasawa2010/19/1537.241141.01333.161.6 ± 1.2713.8 ± 0.33.20 ± 0.241.39 ± 0.7
     Karasuzaki2910/20/1537.686141.01333.115.9 ± 0.403.2 ± 0.21.13 ± 0.319.66 ± 0.9
     Nakaso6610/22/1536.864140.79033.019.7 ± 0.474.4 ± 0.21.90 ± 0.435.29 ± 1.4
    • The Cs activities are decay corrected to the sampling date. BDL, below detection limit; ND, not determined.

    • View popup
    Table S2.

    Activities of 137Cs and 134Cs in sand

    CoreDepth layer, cm137Cs, Bq⋅kg−1Err 137Cs, Bq⋅kg−1134Cs, Bq⋅kg−1Err 134Cs, Bq⋅kg−1
    10–517.30.42.80.2
    5–1022.70.33.90.2
    10–1523.20.33.70.1
    15–2017.80.43.00.2
    20–2522.50.24.00.1
    25–3024.40.34.10.2
    30–3524.30.94.70.5
    35–4019.00.33.10.1
    40–4516.80.32.70.2
    45–5017.90.22.90.1
    50–5519.80.43.00.2
    55–6022.80.43.60.2
    60–6529.40.34.90.1
    65–7036.21.05.90.5
    70–7547.71.47.80.6
    75–8055.21.39.00.6
    20–515.30.22.60.1
    5–1016.90.42.70.2
    10–1513.20.32.20.2
    15–2012.40.52.00.2
    20–2516.40.33.00.2
    25–3018.80.63.00.3
    30–513.60.32.30.1
    5–1011.90.21.70.1
    10–1511.40.32.10.1
    15–2011.20.32.10.2
    20–2511.80.32.00.1
    25–3016.80.42.70.2
    30–3524.80.43.90.2
    35–4026.70.83.80.3
    40–515.00.62.50.0
    5–1015.30.32.60.0
    10–1516.20.42.70.1
    15–2016.50.32.80.1
    20–2515.90.42.50.1
    25–3014.40.62.60.1
    30–3517.10.12.70.0
    35–4019.90.03.30.3
    40–4518.60.02.90.1
    45–5024.00.54.20.1
    50–5525.80.64.50.3
    55–6037.11.76.20.3
    60–6540.90.85.80.5
    65–7028.60.34.60.6
    70–7572.70.911.80.2
    75–805802981
    80–8594011432
    85–90960201605
    90–9586071561
    95–100600101051
    100–10597011701
    • The sand cores were collected at Yotsukura beach on November 2016. The activities are decay corrected to the sampling date and are expressed per kilogram of dry sand.

    • View popup
    Table S3.

    Locations and 137Cs (becquerels per kilogram) activities of sand samples used in the adsorption–desorption experiments

    Mineral phase name content, %
    Beach nameSand ID137Cs activity, Bq⋅kg−1Err 137Cs, Bq⋅kg−1QuartzErrClaysErrAlbiteErrAragoniteErr
    FunatsukeA54452516112620511
    YotsukuraB947426276213103
    YotsukuraC270201435216242102
    • Clay minerals include Muscovite and Montmorillonite from the Mica and Smectite groups, respectively.

    • View popup
    Table S4.

    Volumetric input of submarine groundwater discharge (VGW) estimated using a 223Ra and 244Ra mass balance for the different beaches based on data collected in 2015 and 2016

    VGW, m3⋅m−2⋅d−1224Ra223Ra
    Iwasawa beach 20150.330.44
    Yotsukura beach 20150.210.09
    Karasuzaki beach 20150.120.07
    Nakoso beach 20150.270.21
    Yotsukura beach 20160.510.24

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Unexpected source of Fukushima-derived cesium
Virginie Sanial, Ken O. Buesseler, Matthew A. Charette, Seiya Nagao
Proceedings of the National Academy of Sciences Oct 2017, 114 (42) 11092-11096; DOI: 10.1073/pnas.1708659114

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Unexpected source of Fukushima-derived cesium
Virginie Sanial, Ken O. Buesseler, Matthew A. Charette, Seiya Nagao
Proceedings of the National Academy of Sciences Oct 2017, 114 (42) 11092-11096; DOI: 10.1073/pnas.1708659114
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