Tritium activity concentration and behaviour in coastal regions of Fukushima in 2014

M. Aoyama, S. Charmasson, Y. Hamajima, C. Duffa, D. Tsumune, Y. Tateda
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引用次数: 4

Abstract

Abstract. We observed 3H activity concentrations and the 137Cs activity concentrations during the SoSo 5 rivers cruise in 2014 and at the Tomioka port in 2014–2018. The 3H activity concentrations at coastal stations located close to the Fukushima coast ranged from 90 Bq m−3 to 175 Bq m−3, and decreased between 67 Bq m−3 to 83 Bq m−3 at the stations located 12–16 km from the coast. The 3H activity concentration at the estuaries and ports, except at 56 north canal of the FNPP1 site, are around 200–500 Bq m−3 and slightly lower than the 3H activity concentration of 500–600 Bq m−3 observed in the rivers. These gradients of the 3H activity concentrations in the coastal region might indicate the large effect of 3H flux through the rivers. On the other hand, the 3H activity concentration at 56N of the FNPP1 site was significantly high compared to the 3H activity concentration in surrounding waters both north and south of the FNPP1 site and in river waters. It should also be noted that the 3H activity concentrations were similar at the stations located both north and south of the FNPP1 site, while the 137Cs activity concentrations were lower at the stations north of the FNPP1 site and higher at the stations south of the FNPP1 site. This indicated that the major sources of 137Cs could be the FNPP1 site as the point source while the source of 3H should be more diffuse and linked to riverine inputs located north and south of the FNPP1 site. The 3H / 137Cs activity ratios in coastal waters were 1.2–2.2 as obtained via the slopes by standardised major axis regressions between the 3H activity concentration and the 137Cs activity concentration of SoSo samples and Tomioka Port observed in 2014–2018, which is significantly high compared to that of the released radionuclides derived from the FNPP1 site, which was 0.01 in 2011 just after the accident. The open-water 3H activity concentration contribution to coastal waters was estimated to be 67 ± 20 Bq m−3 and 66 ± 17 Bq m−3 as the intercepts also by standardised major axis regressions. These estimates are consistent with 50 Bq m−3 obtained at the Kuroshio region as the background levels of 3H activity concentration in open water. The 3H and 137Cs fluxes to the coastal region of Fukushima based on the open-water movement, freshwater flux from the rivers based on their respective catchment, and mean monthly precipitation were estimated. The largest 3H flux is the open-water inflow from the north of the FNPP1 site and it reaches 52 GBq day−1, while the rivers north of the FNPP1 site showed 3–5 GBq day−1 fluxes. We obtained a 3H flux as 1.9–4.5 GBq day−1 of 3H using the 3H activity concentration in the port, which is comparable with the fluxes obtained from the rivers located north of the FNPP1 site. While using 3H activity concentration at the 56 north canal of FNPP1, we obtained 28–86 GBq day−1 fluxes, which is one order of magnitude larger than those estimated using 3H activity concentration in the FNPP1 port. One of the reasons could be the very high variability of the 3H levels at 56 north canal and in the port of FNPP1, explaining variable 3H/137Cs activity ratio observed at 56 north canal and in the port of FNPP1. The 3H activity concentration of TFWT in the fish filets collected close to the FNPP1 site ranged from 97 ± 11 Bq m−3 to 144 ± 11 Bq m−3, which were similar to the 3H activity concentrations in the surrounding seawater, in agreement with the knowledge that the bioconcentration factor of 3H is approximately 1. In contrast, higher values were found in TOBT, which can be linked to life-history traits.
2014年福岛沿海地区氚活度浓度及其行为
摘要我们观察了2014年soso5河游船和2014 - 2018年富冈港的3H和137Cs活性浓度。靠近福岛海岸的沿海站点的3H活度浓度在90 ~ 175 Bq m−3之间,距离海岸12 ~ 16 km的站点的3H活度浓度在67 ~ 83 Bq m−3之间。除FNPP1站点的56条北运河外,河口和港口的3H活性浓度在200-500 Bq m−3左右,略低于河流观测到的500-600 Bq m−3。沿海地区3H活度浓度的这些梯度可能表明河流中3H通量的影响很大。另一方面,FNPP1位点56N处的3H活性浓度显著高于FNPP1位点南北周围水域和河流水域的3H活性浓度。值得注意的是,位于FNPP1站点北部和南部的站点的3H活性浓度相似,而FNPP1站点北部站点的137Cs活性浓度较低,而FNPP1站点南部站点的137Cs活性浓度较高。这表明137Cs的主要来源可能是FNPP1位点作为点源,而3H的来源应该更分散,并且与位于FNPP1位点北部和南部的河流输入有关。2014-2018年,通过对SoSo样品和富冈港观测到的3H活性浓度与137Cs活性浓度进行标准化长轴回归,得到沿海水域3H / 137Cs活性比为1.2-2.2,与事故发生后2011年FNPP1站点释放的放射性核素的浓度为0.01相比,这一比例明显较高。开放水域3H活性浓度对沿海水域的贡献估计为67±20 Bq m - 3和66±17 Bq m - 3作为截距,也是通过标准化的长轴回归。这些估计与在黑潮地区获得的50 Bq m−3作为开阔水域3H活性浓度的背景水平是一致的。根据开放水域运动估算了福岛沿海地区的3H和137Cs通量,根据各自的集水区估算了河流的淡水通量,并估计了月平均降水。3H通量最大的是FNPP1站点北部的开放水域流入,达到52 GBq day - 1,而FNPP1站点北部的河流为3-5 GBq day - 1。利用港口的3H活性浓度,我们得到了1.9-4.5 GBq天−1的3H通量,这与位于FNPP1站点以北的河流的通量相当。利用FNPP1北56运河的3H活性浓度,我们获得了28-86 GBq日−1通量,这比利用FNPP1港口的3H活性浓度估计的通量大一个数量级。其中一个原因可能是56号北运河和FNPP1港口的3H水平非常高的可变性,这解释了56号北运河和FNPP1港口观察到的可变3H/137Cs活性比。FNPP1位点附近采集的鱼片中TFWT的3H活性浓度范围为97±11 Bq m−3 ~ 144±11 Bq m−3,与周围海水中3H活性浓度相近,符合3H生物富集因子约为1的认识。相比之下,在TOBT中发现了更高的值,这可能与生活史特征有关。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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