Abstract

The earthquake and tsunami on 11 March 2011 led to a meltdown followed by a hydrogen explosion at the Fukushima–Daiichi nuclear power plant in Japan, causing the dispersal of abundant radionuclides into the atmosphere and ocean. The radionuclides were deposited onto trees and local residences in aerosol or gaseous forms that were partly absorbed by rain or melting snow. Here, we show that the radionuclides attached to the surfaces of trees, in which some radiocesium was incorporated into the xylem through ray cells and through symplastic pathways. The level of incorporated radiocesium varied based on tree species and age because of the ability of radiocesium to attach to the surface of the outer bark. After four years, the radiocesium level in the forest has been decreasing as it is washed out with rainwater into the sea and as it decays over time due to its half-life, but it can also be continuously recycled through leaf tissue, litter, mulch, and soil. As a result, the level of radiocesium was relatively increased in the heartwood and roots of trees at four years after the event. In private forest fields, most trees were left as afforested trees without being used for timber, although some trees were cut down. We discuss an interdisciplinary field study on the immediate effects of high radiation levels upon afforested trees in private forest fields.

Highlights

  • The earthquake and tsunami on March 11, 2011, led to a meltdown followed by a hydrogen explosion at the coastal Fukushima–Daiichi nuclear power plant in Japan, causing the dispersal of high levels of radionuclides into the atmosphere and ocean, resulting in a large amount of environmental damage [1]

  • The deposition pattern of radiocesium was not identical to that of radioiodine [3,4], likely because radiocesium was mainly dispersed in an aerosol form rather than in the gaseous form taken by radioiodine in the Fukushima fallout

  • The radiocesium (134 Cs and 137 Cs) was found at high levels on the outer bark of mulberry (19 years) and cherry (30 years) trees, as shown in Table 2, located on mountainsides facing the radiation epicenter, which were relatively high in elevation

Read more

Summary

Introduction

The earthquake and tsunami on March 11, 2011, led to a meltdown followed by a hydrogen explosion at the coastal Fukushima–Daiichi nuclear power plant in Japan, causing the dispersal of high levels of radionuclides into the atmosphere and ocean, resulting in a large amount of environmental damage [1]. Cs-134, the most serious damaging fallout to date has involved radiocesium and radioiodine [2]. The deposition pattern of radiocesium was not identical to that of radioiodine [3,4], likely because radiocesium was mainly dispersed in an aerosol form rather than in the gaseous form taken by radioiodine in the Fukushima fallout. In Fukushima, the radiation levels were 150 times levels for radiocesium and three times for radioiodine, which are larger than the levels after the atomic bombing of Hiroshima, but one-fifth and one-tenth, Forests 2019, 10, 652; doi:10.3390/f10080652 www.mdpi.com/journal/forests

Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call