Sr and 89 Sr in seawater off Japan as a consequence of the Fukushima Dai-ichi nuclear accident

The impact of the earthquake and tsunami on the east coast of Japan on 11 March 2011 caused a loss of power at the Fukushima Dai-ichi nuclear power plant (NPP) that resulted in one of the most important releases of artificial radioactivity into the environment. Although several works were devoted to evaluating the atmospheric dispersion of radionuclides, the impact of the discharges to the ocean has been less investigated. Here we evaluate the distribution of Fukushima-derived 90 Sr ( n = 57) and 89 Sr ( n = 19) throughout waters 30–600 km offshore in June 2011. Concentrations of 90 Sr and 89 Sr in both surface waters and shallow profiles ranged from 0.8 ± 0.2 to 85 ± 3 Bq m −3 and from 19 ± 6 to 265 ± 74 Bq m −3 , respectively. Because of its short half-life, all measured 89 Sr was due to the accident, while the 90 Sr concentrations can be compared to the background levels in the Pacific Ocean of about 1.2 Bq m −3 . Fukushima-derived radiostrontium was mainly detected north of Kuroshio Current, as this was acting as a southern boundary for transport. The highest activities were associated with near-shore eddies, and larger inventories were found in the closest stations to Fukushima NPP. The data evidence a major influence of direct liquid discharges of radiostrontium compared to the atmospheric deposition. Existing 137 Cs data reported from the same samples allowed us to establish a 90 Sr / 137 Cs ratio of 0.0256 ± 0.0006 in seawater off Fukushima, being significantly different than that of the global atmospheric fallout (i.e., 0.63) and may be used in future studies to track waters coming from the east coast of Japan. Liquid discharges of 90 Sr to the ocean were estimated, resulting in an inventory of 53 ± 1 TBq of 90 Sr in the inshore study area in June 2011 and total releases of 90 Sr ranging from 90 to 900 TBq, depending upon the reported estimates of 137 Cs releases that are considered.


Introduction
Radiostrontium, and in particular 90 Sr (T 1/2 = 28.9a), is an artificial radionuclide that has been liberated to the environment in the last decades mainly due to the atmospheric nuclear weapon testing performed in the 1950s and 1960s and the direct releases into the sea from nuclear reprocessing facilities.Given that oceans cover more than 70 % of the Earth's surface, much of these releases of 90 Sr now remain dissolved into seawater (IAEA, 2005).Concentrations of 90 Sr in oceans are summarized in the World Marine Radioactivity Studies (WOMARS), and a global 137 Cs / 90 Sr ratio of 1.5 has been established.As its chemical behavior is similar to that of calcium, strontium is deposited in biological systems, especially in those tissues with high calcium content such as bone.The highly energetic 0.546 MeV beta particles, and the additional exposure to the 2.2 MeV beta particles released during decay of its short-lived 90 Y daughter isotope, make 90 Sr a radionuclide of health concern (ICRP, 1993).However, not much literature exists on the presence of 89 Sr (T 1/2 = 50.52d) in the oceans.This radionuclide is also a primary fission product, but with a much shorter halflife than 90 Sr.
As a result of the earthquake on 11 March 2011, and subsequent tsunami, radionuclide contaminants were accidently released into the environment from the Fukushima Dai-ichi nuclear power plant (NPP).The emissions of artificial radionuclides both to the atmosphere (Chino et al., 2011) and the marine environment (i.e., Povinec et al., 2012;Buesseler et al., 2011) have been broadly reported.In particular, 134 Cs and 137 Cs concentrations at the nuclear power plant ocean discharge channels peaked in early April at levels that reached several millions times higher compared with the preexisting levels in this area (Buesseler et al., 2011), thus representing the most important accidental artificial radioactive release into the sea (Bailly du Bois et al., 2011).Simulations of regional ocean models using 137 Cs concentrations in the ocean off Fukushima allowed estimating the total amount of 137 Cs directly discharged to the ocean, ranging from 1 to more than 20 PBq (Kawamura et al., 2011;Tsumune et al., 2012;Bailly du Bois et al., 2011).
Although temporal changes of 131 I, 134 Cs and 137 Cs concentrations in surface water adjacent to Fukushima have been well documented, releases of radiostrontium into the sea are poorly investigated (Povinec et al., 2012).The main reason for this lack of data resides in the difficulties of preconcentrating and analyzing 90 Sr in seawater.The recent study by Povinec et al. (2012) was the first report assessing the impact of radiostrontium released from the Fukushima Dai-ichi nuclear power plant into the marine environment.Their data on 90 Sr in coastal seawater (near the discharging channel in Fukushima Dai-ichi NPP) were obtained from the Ministry of Education, Culture, Sports, Science and Technology (MEXT).Concentrations of 90 Sr reached up to four orders of magnitude greater than the pre-Fukushima levels (1.2 Bq m −3 ).Between March and November 2011, maxima activities of 90 Sr and 89 Sr were of 69 and 9.3 kBq m −3 , respectively, but even higher values were reported after a December 2011 accidental discharge (400 and 140 kBq m −3 for 90 Sr and 89 Sr, respectively) (Povinec et al., 2012).
This study is part of an international project, which aimed at understanding the amount, type and fate of radioactive materials released into the northwest Pacific Ocean and to see whether the Kuroshio Current was acting as a southern boundary for radionuclide transportation in the marine environment.This is the first survey of 90 Sr and 89 Sr offshore Japan after the Fukushima NPP accident in March 2011.In particular, here we evaluate the distributions of 90 Sr and 89 Sr released from Fukushima into the water column in an area encompassing 30-600 km off Japan in May-June 2011.

Seawater sampling
A total of 57 20 L seawater samples, both from surface and vertical profiles, were collected from the R/V Ka'imikai-o-Kanaloa (KOK) between 4 and 18 June 2011 (Fig. 1).Sample codes, collection date, locations, depths, salinity and temperature of each sample are provided in Table 1.
Surface waters were collected using a deck-mounted pump and hose, which was placed about 2 m below the sea surface.A pre-filter cartridge was used to remove the suspended matter.Deeper samples (10-200 m) were collected with Niskin bottles mounted on a CTD/Rosette at stations #3, #19, #21, #23, #25, #27 and #29 (see Table 1).Samples were spiked with 200 mg of Sr 2+ and stored for its subsequent analysis at the Universitat Autònoma de Barcelona and Universidad de Sevilla.

90 Sr purification and quantification through 90 Y counting by proportional counter
Once in the laboratory, samples were weighted and acidified with concentrated HCl.The purification method for the analysis of 90 Sr was based on the protocol described in Waples and Orlandini (2010), and adapted to seawater samples by Casacuberta et al. (2013).The method consists in the measurement of the daughter of 90 Sr, 90 Y (T 1/2 = 64 h), which is in equilibrium with 90 Sr, by beta counting.Samples were spiked with 10 mg of stable Y, and 30 mg of Fe 3+ as ferrous sulfate was added to the samples.After letting samples equilibrate overnight, pH was raised up to 8 to coprecipitate yttrium with the iron hydroxides.The precipitate was then collected onto a nitrocellulose filter (0.22 µm, 14 cm, Whatman) and subsequently dissolved in 20 mL HNO 3 8 M. Isolation of yttrium from other beta emitters (mainly Th) was performed by passing the solution through an anion ionexchange column (Bio-Rad AG1-X8, 100-200 mesh).The eluate, 40 mL of HNO 3 8 M, was then evaporated to reconstitute the sample in 20 mL 1 M HCl.A further separation on a cation exchange column (Bio-Rad AG50W-X8, 100-200 mesh) was required for the final purification of yttrium from lead isotopes.Sample was transferred to the column and 80 mL of 1 M HCl were added to wash the resin.Finally, yttrium was eluted by adding 30 mL 6 M HCl recovered by precipitation using ferric hydroxides and filtration onto a nitrocellulose filter (0.22 µm, 47 mm, Whatman), which was dried and placed onto a beta holder for the measurement of the 90 Y beta emissions.Samples were measured on a 5-position beta counter manufactured by RISØ National Laboratories (Roskilde, Denmark) during 60 min intervals over approximately 60-64 h.Filters were re-measured after 1 week and 3 weeks to verify that detected counts corresponded to the decay of 90 Y and no other beta emitters, including 91 Y (halflife: 58.5 d), interfered.Yttrium chemical recoveries (that  1 for more details), superimposed on surface velocities (from Buesseler et al., 2012).Grey contour on the left represents the Japan coast, whereas the red star stands for the Fukushima Dai-ichi NPP.
ranged from 10 to 85 %) were assessed by determining the stable Y concentrations by ICP-MS.

89 Sr purification and quantification by proportional counter
The supernatants from the first separation of iron hydroxides described in Sect.2.2 were stored and sent to Universidad de Sevilla to proceed with an alternative direct determination of 90 Sr in the same samples.The initial objective was to perform these measurements as a quality control exercise to validate the results obtained by the method described previously in Sect.2.2.However, the method used for the validation of 90 Sr allowed for the determination of both 89 Sr and 90 Sr (the first one only measured in some samples due to the long time delay between sampling and measuring).
The conventional radiochemical procedure (Harvey et al., 1989) applied for isolation and purification of the 89 Sr and 90 Sr in the supplied supernatants was based in an initial oxalate precipitation, followed by a transformation of the oxalate precipitate into carbonate by calcination to 550 • C. Subsequently, calcium was mostly eliminated by fuming acid precipitation, followed by the dissolution of the precipitate in water, its evaporation to dryness and its posterior redissolution in nitric acid.
Barium was afterwards separated from strontium by formation of barium chromate precipitation, and yttrium was removed by two successive hydroxide precipitations.Strontium was finally purified by its precipitation with a saturated solution of sodium carbonate, subsequent conversion of the precipitate to strontium nitrate by adding concentrated HNO 3 , the dissolution of the precipitate with hot water, and the final precipitation of the Sr as SrCO 3 , by adding again a saturated solution of sodium carbonate.The final SrCO 3 precipitate was homogeneously distributed over the counting planchet and dried until constant weight in a desiccator.
The radiochemical yields were determined gravimetrically and double-checked by ICP-MS in a selected number of samples.The presence of natural Sr in samples was considered after its determination in aliquots by ICP-MS.
The quantification of 89 Sr and 90 Sr was performed by using a 10-channel low-level proportional counter (LB790, Berthold Technologies).Two measurements at different time intervals were performed to determine the concentrations of 89 Sr and 90 Sr in the sample under study at the time of sampling.The first one was performed 36-72 h just after the 90 Y separation and the second one at least 18 days after the first measurement.In all cases, each measurement was performed during at least two cycles of 600 min.From the net counting rates obtained in the two measurements, the activities of 89 Sr and 90 Sr were determined, following the methodology described in Herranz et al. (2011), which implies the previous calibration of the counter for determination of the counting efficiencies of 90 Sr, 90 Y and 89 Sr.

90 Sr in surface seawaters
Activities of 90 Sr in surface seawater samples ranged from 1.1 ± 0.2 to 85 ± 3 Bq m −3 .The highest concentrations were found along the northern coast of Japan, being particularly enhanced about 100-200 km SE from Fukushima, at stations 29 and 30 (Fig. 2a).The concentration of 90 Sr in surface samples from near-shore stations ranged from 10 to 85 Bq m −3 .The lowest activities were located in the southeastern areas of the studied area (i.e., stations 1, 2, 3 and 10) and northern from Fukushima NPP (stations 20 and 24).These concentrations were close to the background value of 1.2 Bq m −3 reported for this area before the Fukushima NPP accident (IAEA, 2005).The distribution pattern of 90 Sr concurs with the surface 137 Cs and 134 Cs dispersal reported in Buesseler et al. (2012), from the same cruise (Fig. 2b and c).

90 Sr in shallow profiles
Specific activities of 90 Sr in shallow profiles (down to 200 m) taken at stations 19, 21, 23, 25, 27 and 29 are detailed in Table 1 and summarized in Fig. 3.In all cases, the majority of 90 Sr was found in the first 50 m depth horizon.In general, 90 Sr concentrations measured at the deepest waters of each profile correspond to the expected for background levels (1.2 Bq m −3 ) of 90   The particular behavior of 90 Sr at stations 23 and 25 corresponds to an area affected by near-shore eddies.This is observed in the section represented in Fig. 4a, which comprises stations 25 (left), 23, 21, 19 and 11 (right). 90Sr concentrations at station 23 are significantly higher (from 5 to 37 Bq m −3 ) than the concentrations in the two profiles closer to shore (stations 25 and 21), due to the presence of this nearshore eddy (see Fig. 4b and c).Distribution of 90 Sr according to water masses is further discussed in Sect.4.2.
Inventories of 90 Sr in the upper 100 m were calculated for the six profiles located closer to the coast (Fig. 5).These inventories were in all instances higher than the expected inventory of 90 Sr for this area prior to the Fukushima acci-dent, calculated assuming a background 90 Sr concentration of 1.2 Bq m −3 in the water column (i.e., 120 Bq m −2 ).Station 23 holds the greatest inventory of 90 Sr (2511 ± 102 Bq m −2 ), followed by stations 27 and 29, these last ones corresponding to the stations that presented the highest 90 Sr concentrations at surface.

89 Sr results in surface and shallow profiles
89 Sr was quantified in 19 samples (Table 1), and concentrations ranged from 19 ± 6 to 265 ± 74 Bq m −3 in surface waters, reaching a maximum subsurface value of 137 ± 43 Bq m −3 at 50 m depth at station 23.Due to the short half-life of 89 Sr (50.53 d) and the long time delay between sampling and counting (up to 5-6 months), uncertainties were larger than 40 % in some of the measured samples.

Impact of the Fukushima Dai-ichi nuclear accident in seawaters off Japan
Contrary to other radionuclides such as 137 Cs, 134 Cs and 131 I (Hisamatsu, 2012), the amounts of radiostrontium in the form of liquid radioactive wastes released into the sea after the Fukushima Dai-ichi nuclear accident are less known, mostly due to the more complex and time-consuming analytical procedures used for its determination.However, as the cooling water directly interacted with ruptured nuclear fuel rods, large amounts of radiostrontium may have been released directly into the ocean as well (Povinec et al., 2012).Indeed, our results of 90 Sr and 89 Sr in both surface seawater and depth profiles showed a clear impact of the Fukushima nuclear accident in the waters off Japan.Before April 2011, the main 90 Sr source in the Japanese waters was due to global fallout from atmospheric weapons testing, including the influence of 11 Chinese atmospheric nuclear weapons tests in the 1970s (Ikeuchi, 2003).Just after these events, the average 90 Sr concentrations on the eastern coast off Japan were between 4.3 and 5.7 Bq m −3 .Average concentrations measured during the 1980s and 1990s ranged between 2.5 and 2.8 Bq m −3 , and the last 90 Sr concentrations reported ranged from 1.4 to 1.8 Bq m −3 in surface waters (Ikeuchi et al., 1999 andPovinec et al., 2010) and between 0.21 and 0.58 Bq m −3 in deep waters (> 2000 m) (Ikeuchi et al., 1999).Decaycorrected concentrations of 90 Sr in the West Pacific Ocean in 2011 would therefore have decreased to a range of 1.1 to 1.4 Bq m −3 (IAEA, 2005;Povinec et al., 2012), agreeing with the lowest value found in this study for surface waters (i.e., 1.1 ± 0.2 Bq m −3 ).The Fukushima Dai-ichi nuclear accident produced an increase of the 90 Sr concentrations in the waters off Japan, such that three months after the accident they were 1 to 2 orders of magnitude higher than the background in some areas.Fukushima-derived radiostrontium was present not only in surface waters but also at depth, reaching maximum values of 37 ± 3 Bq m −3 at 20 m.The presence of 90 Sr in the waters off Japan derived from the Fukushima nuclear accident was accompanied by the presence of 89 Sr.Given its short half-life (50.57d), the occurrence of this radionuclide is a faultless signal of the Fukushima-derived release.Moreover, the 89 Sr / 90 Sr ratio pointed to be Fukushima-derived radiostrontium, as the decay-corrected ratio measured in this study (see Sect. 4.3) is in excellent agreement with the ratio reported for the reactor core inventory on 11 March 2011(Nishikara et al., 2012).

Distribution of 90 Sr on the coast off Japan
Three assumptions were made for discussing the 90 Sr distribution in the waters off Japan in May-June 2011: (i) the Sr peak in direct oceanic release into the Pacific Ocean took place on 6 April, as it did for Cs isotopes (Buesseler et al., 2011); (ii) both Cs and Sr behave geochemically similarly (Fig. 2) in the waters off Japan, as both are dissolved in seawater and have a weak interaction to sediment (IAEA, 2005;Povinec et al., 2003); and (iii) most of the 90 Sr left in the KOK sampling area at the time of the cruise came from the direct oceanic discharges, as it was the case for Cs (Rypina et al., 2013, this issue).
After the radionuclide peak release, 90 Sr in seawaters would be dispersed and distributed through the Japanese coast governed by advection processes occurring in this specific area of the Pacific Ocean.In particular, this is a region where three main currents converge: the Oyashio, the Kuroshio and the Tsugaru currents (Talley et al., 1995).The Oyashio front is defined as the southern limit of subpolar waters with very low salinity, which are driven from the northern to the southern coast of Japan (Fig. 6).The Kuroshio Current originates in the subtropical gyre, consisting of low density, warm, high salinity surface waters, coming from the southwest of the Japanese coast (Fig. 6).Finally, the Tsugaru Current (not present in May-June) is a source of warm and saline water that enters the Sea of Japan through the Tsushima and Tsugaru straits (Talley et al., 1995).
Using data from surface drifters released during the KOK cruise, Rypina et al. (2013, this issue) performed a numerical model to investigate the dominant mechanisms governing the short-term spread of radionuclides in this area.From their model, and similar to 137 Cs results, the following can be stated: (i) the absence of the 90 Sr at the southernmost stations (stations 1, 2, 3, 14 and 28) was attributed to the Kuroshio Current, which prevents a southward progression of Fukushima contaminants such as 90 Sr; (ii) the largest concentration of 90 Sr was shown to be associated with the semipermanent near-shore eddy and stirring them for a long time around the eddy perimeter (stations 29, 30 and 31); and (iii) the intermediate 90 Sr concentrations at the westernmost row of stations (stations 25 and 27) were explained by the coolant water that continued to leak from the reactor after the peak release.
In addition to the dispersion of radiostrontium in surface waters off Japan, 90 Sr may also have penetrated into deep waters, either by diffusion or advection processes, as shown by our measurements of Fukushima-derived radiostrontium down to 100-200 m depth.

89 Sr / 90 Sr ratio
The 89 Sr / 90 Sr net ratio (subtracting 90 Sr background concentrations) can be used to estimate the time delay between sampling and the Fukushima accident (time of nuclear reactor cease).Although the date of the nuclear accident was well known, the ratio was used to corroborate it and thus prove the 89 Sr source being Fukushima NPP in a sort of academic exercise.Time delay calculated for each sample (Table 2) was estimated by using the following Eq.( 1 where ( 89 Sr / 90 Sr) obs is the net ratio measured at each sample at sampling time, ( 89 Sr / 90 Sr) reactor the ratio at reactor (i.e., 11.8 ± 0.4 according to Povinec et al., 2012), and λ89 Sr the decay constant of 89 Sr (0.0137 d −1 ).Resulting values range from 74 to 135 d, which on average is 98 ± 18 d and is in good agreement with the elapsed time since the accident.

Estimate of 90 Sr discharge to the sea
Several works have been devoted to quantifying the amount of 137 Cs released into the sea due to the Fukushima Dai-ichi nuclear accident, ranging from 3.5 to 34 PBq (Tsumune et al., 2012;Buesseler et al., 2012;Bailly-du-Bois et al., 2012;Charette et al., 2013, this issue).Here we calculated the release of 90 Sr by using the 90 Sr / 137 Cs ratio data obtained from the analyzed samples (Buesseler et al., 2012), once  corrected for background concentrations (1.2 and 2.5 Bq m −3 for 90 Sr and 137 Cs, respectively) (IAEA, 2005) (Fig. 7).The 90 Sr / 137 Cs ratio for the samples collected during the KOK cruise was 0.0265 ± 0.0006, which is higher than the ratio of 0.01 reported by Povinec et al. (2012).Their value was the average of the data obtained in April 2011 at site 1, close to one of the discharging channels.Indeed if calculating the average value at their sites 1 and 2 (close to discharging chan-nels), 7 and 8 (15 km off the Fukushima NPP) between April and June, the resulting ratio 90 Sr / 137 Cs is 0.0282, in very good agreement with our data.Therefore, ratio 90 Sr / 137 Cs calculated here (0.0265 ± 0.0006) is representative of the average ratios found in Povinec et al. (2012) once surface waters off the coast of Japan were homogenized.The total amount of 90 Sr in the study area in June 2011, taking the inventory of 2 PBq of 137 Cs estimated by Buesseler et al. (2012) and using the 90 Sr / 137 Cs ratio of 0.0265 ± 0.0006, would then be of 53 ± 1 TBq.This figure is constrained within the inshore box, but the actual total releases of 90 Sr would have been greater.Given the range of published estimates of 137 Cs releases due to direct discharge from the NPP, the total amount of 90 Sr released could range from 90 to 900 TBq (Table 3).
It is worth noticing that in December 2011, the Tokyo Electric Power Company reported an accidental leakage from the evaporative condensation apparatus at Fukushima Daiichi NPP of approximately 150 L of water containing 11 GBq of 89 Sr and 15 GBq of 90 Sr.In fact, activities of 90 Sr measured at the discharge site in December 2011 exceeded 137 Cs concentrations.Thus the 90 Sr / 137 Cs ratio that we measured cannot be used to predict the total amounts of 90 Sr released through direct ocean discharge after December 2011.
The amount of 90 Sr released because of the Fukushima Dai-ichi NPP accident can be compared with the most important nuclear accidents and the discharges of nuclear reprocessing fuel plants.The releases of 90 Sr from Chernobyl were quantified in 10 PBq (IAEA, 2003), of which 277 TBq were discharged to the Black Sea through the Pripyat and Dnieper rivers (Vakulovsky et al., 1994).However, the direct inputs to the ocean were considered to be negligible as the radioactivity release was mainly of atmospheric origin (IAEA, 2005).On the contrary, 90 Sr releases into the Pacific Ocean

Direct releases of 90 Sr into the sea versus atmospheric deposition
The amount of radiostrontium measured in the study area during the KOK cruise could be a result of two main sources: (i) the localized direct discharge of contaminated coolant waters into the near-shore ocean, and (ii) the fallout of airborne discharge released into the atmosphere during the Fukushima NPP explosions, with subsequent deposition onto the ocean.Strontium is much less volatile than other fission products such as cesium and iodine isotopes, and thus smaller amounts of 90 Sr compared to 137 Cs were expected to be released into the atmosphere.Indeed, TEPCO published a 90 Sr / 137 Cs ratio in soils of 0.001, which is far below the average ratio measured in seawater in this study (i.e., 0.0265).If the 90 Sr / 137 Cs ratio of liquid discharges in April-May 2011 was 0.0265 and the ratio from atmospheric release was 0.001, it is clear that the ocean samples had a much stronger influence of the direct discharges of cooling water into the sea www.biogeosciences.net/10/3649/2013/Biogeosciences, 10, 3649-3659, 2013 and the oceanic background concentration reported for the Pacific Ocean before Fukushima NPP accident (Fig. 8).

Conclusions
This study is the first survey of 90 Sr and 89 Sr offshore Japan after the Fukushima NPP accident in March 2011.Concentrations of 90 Sr and 89 Sr detected at 32 stations, including both surface and shallow profiles, ranged from 0.8 ± 0.2 to 85 ± 3 Bq m −3 and from 19 ± 6 to 265 ± 74 Bq m −3 , respectively.While the occurrence of 89 Sr is an evident signal of Fukushima-derived releases, the activities of 90 Sr measured in some stations reached values two orders of magnitude higher than the background levels reported in this area (i.e., 1.2 Bq m −3 ).The 90 Sr / 137 Cs ratio has been calculated to be 0.0265 ± 0.0006 (in May-June 2011) although it may have varied, especially after a significant leakage of contaminated waters that occurred in December 2011.This ratio is unique and significantly different than that of the global atmospheric fallout produced by nuclear weapon tests, which was 0.63, and it may be used in future studies to track waters coming from Fukushima.Results of the samples analyzed here evidenced a much stronger influence of direct discharges of cooling water into the sea and the oceanic background concentration, rather than atmospheric deposition.Direct discharges have been quantified on the basis of the estimates of 137 Cs discharges and the 90 Sr / 137 Cs ratio, resulting in a range between 90 and 900 TBq of 90 Sr.

Fig. 1 .
Fig. 1.Sampling stations, with their corresponding station numbers (see Table1for more details), superimposed on surface velocities (fromBuesseler et al., 2012).Grey contour on the left represents the Japan coast, whereas the red star stands for the Fukushima Dai-ichi NPP.

Fig. 2 .
Fig. 2. (a) Activities of 90 Sr in surface seawater samples (expressed in Bq m −3 ).Grey contour on the left represents the Japanese coast.The red star stands for the Fukushima NPP.The right-hand plots show the specific activity of 137 Cs (b) and 134 Cs (c) in surface waters from Buesseler et al. (2012).

Fig. 3 .
Fig. 3. Specific activities of 90 Sr in shallow profiles at the 6 closest stations of Fukushima Dai-ichi NPP.Note the different scales on the x-axis.

Fig. 5 .
Fig. 5.Total inventories of 90 Sr in the upper 100 m of the water column at stations 19, 21, 23, 25, 27 and 29.The solid line represents the background value for this area (120 ± 40 Bq m −2 ), and the numbers above the bars indicate the Fukushima-derived inventory (subtracting the background).

Fig. 6 .
Fig. 6.Surface salinity and temperature measured during the KOK cruise in June 2011; the Oyashio and Kuroshio currents are depicted.Grey contour on the left represents the Japanese coast.

Fig. 8 .
Fig. 8.The 90 Sr / 137 Cs ratio as a function of 137 Cs specific activities.The grey dashed line represents the oceanic background ratio decay corrected to 2011.Also shown are the 90 Sr / 137 Cs ratios corresponding to the oceanic background ratio, the direct discharges from Fukushima Dai-ichi and the atmospheric deposition.

Table 1 .
Concentrations of90Sr and 89 Sr in seawater samples collected off Fukushima in June 2011.Information on collection date location, depth, salinity and temperature is also provided.All activities refer to sampling date.90Sractivities reported here correspond exclusively to the samples measured following the method described in Sect.2.2.

Table 3 .
Amounts of90Sr released into the sea from the Fukushima NPP by June 2011, in TBq (× 10 12 Bq), calculated using the published estimates of 137 Cs releases and a 90 Sr / , 137 Cs ratio of 0.0265 ± 0.0006.The leakage 90 Sr occurred in December 2011 is not included in these estimates.