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Development of Freshwater Foodchain Model for Calculating Tritium Transfer in Aquatic Organisms in Freshwater Following Nuclear Accident

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2019 ⦽ǎႊᔍᖒ⠱ʑྜྷ⦺⫭ ⇹ĥ⦺ᚁݡ⫭ םྙ᫵᧞Ḳ

355

Development of Freshwater Foodchain Model for Calculating Tritium Transfer in

Aquatic Organisms in Freshwater Following Nuclear Accident

Sora Kim, Kyung-suk Suh*, Byung-Il Min, Kihyun Park, Byung-Mo Yang, and Jiyoon Kim

Korea Atomic Energy Research Institute, 111, Daedeok-daero 989beon-gil, Yuseong-gu, Daejeon, Republic of Korea *

[email protected]

1. Introduction

In the field of radiation protection, tritium was not major concern, because the radiological impact of tritium is not significant comparing with other radionuclides. Interest in tritium has grown after the experience of the release of tritium from the Fukushima Daiichi Nuclear Power Plant accident [1, 2] and the high OBT (Organically bound tritium) level measured in aquatic organisms [3, 4]. Tritium can pose a health hazard due to internal exposure via inhalation or ingestion, but health effect of external exposure could be negligible.

A model has been developed to estimate tritium concentrations in aquatic organisms and the effect on human health. Calculation was performed on the Fukushima accident case.

2. Materials and Methods

2.1 Aquatic Food Chain Model for Tritium

The model calculates the OBT and HTO (tritiated water) transfer through the aquatic food chain following accidental releases of tritium. It is based on a dynamic model for OBT and an equilibrium model for HTO. It considers 4 types of aquatic organisms: phytoplankton, zooplankton, prey fish, and predatory fish.

2.2 Input Data and Assumptions for Calculation

Measurement data of tritium concentration at Hiso River in Iitate village from 2011 to 2014 were taken from Ueda et al. (2015) [5].

Fig. 1. Sampling location of Rivers in Fukushima prefecture. Figure taken from Ueda et al. (2015) [5].

Fig. 2. H-3 concentration in Hiso river water. Data taken from Table 1 of Ueda et al. (2015) [5].

3. Results and Discussion

River water in some regions of Japan have been contaminated with radionuclides released from Fukushima Daiichi nuclear power plant (FDNPP)

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2019 ⦽ǎႊᔍᖒ⠱ʑྜྷ⦺⫭ ⇹ĥ⦺ᚁݡ⫭ םྙ᫵᧞Ḳ accident. We calculated HTO and OBT concentration in aquatic organisms which were inhabited at Hiso River in Iitate village in Fukushima Prefecture from 2011 to 2014. Fig. 3 (a) and (b) show the predicted activity concentrations of H-3 in 4 types of aquatic organisms at Hiso River for two cases: 1) the use of mean background H-3 concentration (0.4 Bq/L) in river water, 2) use of fitting data (contaminated by FDNPP accident) presented in Fig. 2. About 1,200 ~ 1,400 days after the Fukushima accident, concentration levels of H-3 in aquatic organisms inhabited at Hiso River become similar to those aquatic organisms inhabited at rivers with background levels of H-3. OBT concentration was predicted to account for less than about 5% of H-3 concentration in aquatic organism.

Fig. 3. (a) H-3 (HTO+OBT) and (b) OBT concentration in aquatic organisms in Hiso River from 2011 to 2014.

4. Conclusions

A tritium aquatic food chain model was recently developed to estimate tritium transfer through the aquatic food chain and the resulting radiological impact on the public following accidental releases.

Comparative analysis with monitoring data and simulation results from other model will be conducted after collecting sufficient data. The developed tritium aquatic food chain model will be used as a tool to estimate contaminated levels of aquatic food and ingestion doses for accidentally release of tritium.

ACKNOWLEGEMENT

This work was supported by the National Research Foundation of Korea (NRF) and funded by the Korea government (MSIP) (MSIP: NRF-2017M2A8A4015253, NRF-2015M2A2B20342 82).

REFERENCES

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H in plants around Fukushima Dai-ichi Nuclear Power 6WDWLRQ 6FLHQWLILF 5HSRUWV´    GRL 10.1038/srep00947 (2012).

>@ 1 7DNDKDWD HW DO ³'LUHFW WULWLXP HPLVVLRQV WR the ocean from the Fukushima Dai-ichi nuclear DFFLGHQW´*HRFKHPLFDO-RXUQDOGRL geochemj.2.0499 (2018).

>@ $ 0HOLQWHVFX ' *DOHULX ³'\QDPLF PRGHO IRU WULWLXPWUDQVIHULQDQDTXDWLFIRRGFKDLQ´5DGLDW Environ Biophys, 50:459-473 (2011).

[4] F. Eyrolle-%R\HUHWDO³$SSDUHQt enrichment of organically bound tritium in rivers explained by WKH KHULWDJH RI RXU SDVW´ - (QYLURQ 5DGLRDFW 136:162-168 (2014).

>@ 6 8HGD HW DO ³1XFOHDU DFFLGHQW-derived 3H in river water of Fukushima Prefecture during 2011-´-(QYLURQ5DGLRDFt. 146:102-109 (2015).

수치

Fig. 2. H-3 concentration in Hiso river water. Data taken  from Table 1 of Ueda et al
Fig. 3. (a) H-3 (HTO+OBT) and (b) OBT concentration in  aquatic organisms in Hiso River from 2011 to 2014

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