Soil decontamination, which began in 2013 following the accident at the Fukushima Dai-ichi nuclear power plant, has now been nearly completed in the priority areas identified[1]. Indeed, areas that are difficult to access have not yet been decontaminated, such as the municipalities located in the immediate vicinity of the nuclear power plant. Olivier Evrard, a researcher at the Laboratory of Climate and Environmental Sciences and coordinator of the study (CEA/CNRS/UVSQ), in collaboration with Patrick Laceby of Alberta Environment and Parks (Canada) and Atsushi Nakao of Kyoto Prefecture University (Japan), compiled the results of approximately sixty scientific studies published on the topic.
Map of Fukushima prefecture (showing the special
decontamination zone, SDZ, delineated in red), the intensive contamination
areas where monitoring is conducted (ICAs, grey areas). FDNPP: Fukushima
This synthesis focuses mainly on the fate of radioactive cesium in the environment because this radioisotope was emitted in large quantities during the accident, contaminating an area of more than 9,000 km2. In addition, since one of the cesium isotopes (137Cs) has a half-life of 30 years, it constitutes the highest risk to the local population in the medium and long term, as it can be estimated that in the absence of decontamination it will remain in the environment for around three centuries. "The feedback on decontamination processes following the Fukushima nuclear accident is unprecedented, according to Olivier Evrard, because it is the first time that such a major clean-up effort has been made following a nuclear accident. The Fukushima accident gives us valuable insights into the effectiveness of decontamination techniques, particularly for removing cesium from the environment".
This analysis provides new scientific lessons on decontamination strategies and techniques implemented in the municipalities affected by the radioactive fallout from the Fukushima accident. This synthesis indicates that removing the surface layer of the soil to a thickness of 5 cm, the main method used by the Japanese authorities to clean up cultivated land, has reduced cesium concentrations by about 80% in treated areas. Nevertheless, the removal of the uppermost part of the topsoil, which has proved effective in treating cultivated land, has cost the Japanese state about €24 billion. This technique generates a significant amount of waste, which is difficult to treat, to transport and to store for several decades in the vicinity of the power plant a step that is necessary before it is shipped to final disposal sites located outside Fukushima prefecture by 2050. By early 2019, Fukushima's decontamination efforts had generated about 20 million cubic metres of waste.
Overviews of various decontaminated areas, used either for temporary storage of contaminated land or for crop recultivation experiments (rice, middle; flowers, right).
© Olivier Evrard, J. Patrick Laceby, and Atsushi Nakao
Decontamination activities have mainly targeted agricultural landscapes and residential areas. The review points out that the forests have not been cleaned up - because of the difficulty and very high costs that these operations[2] would represent - as they cover 75% of the surface area located within the radioactive fallout zone. These forests constitute a potential long-term reservoir of radiocesium, which can be redistributed across landscapes as a result of soil erosion, landslides and floods, particularly during typhoons that can affect the region between July and October. Atsushi Nakao, co-author of the publication, stresses the importance of continuing to monitor the transfer of radioactive contamination at the scale of coastal watersheds that drain the most contaminated part of the radioactive fallout zone. This monitoring will help scientists understand the fate of residual radiocesium in the environment in order to detect possible recontamination of the remediated areas due to flooding or intense erosion events in the forests.
The analysis recommends further research on:
the issues associated with the recultivation of decontaminated agricultural land[1],
the monitoring of the contribution of radioactive contamination from forests to the rivers that flow across the region,
and the return of inhabitants and their reappropriation of the territory after evacuation and decontamination.
Complementary approaches conducted by the CEA
This research is complementary to the project to develop bio- and eco-technological methods for the rational remediation of effluents and soils, in support of a post-accident agricultural rehabilitation strategy (DEMETERRES), led by the CEA, and conducted in partnership with INRA and CIRAD Montpellier.
Decontamination techniques
- In cultivated areas within the special decontamination zone, the surface layer of the soil was removed to a depth of 5 cm and replaced with a new "soil" made of crushed granite available locally. In areas further from the plant, substances known to fix or substitute for radiocesium (potassium fertilizers, zeolite powders) have been applied to the soil.
- As far as woodland areas are concerned, only those that were within 20 metres of the houses were treated (cutting branches and collecting litter).
- Residential areas were also cleaned (ditch cleaning, roof and gutter cleaning, etc.), and (vegetable) gardens were treated as cultivated areas.
[1] In Fukushima prefecture and the surrounding prefectures, the decision to decontaminate the landscapes affected by the radioactive fallout was made in November 2011 for 11 districts that were evacuated after the accident (special decontamination zone - SDZ - 1,117 km 2) and for 40 districts affected by lower, but still significant levels of radioactivity and that had not been evacuated in 2011(areas of intensive monitoring of the contamination - ICA, 7836 km2).
[2] 128 billion euros according to one of the studies appearing in the review to be published on 12 December 2019 in SOIL.
[3] Relating to soil fertility and the transfer of radiocesium from the soil to plants, for example.