On the one-year anniversary of the
nuclear accident in Fukushima radiation in the ocean yet to reach Hawaii
by Henrieta
Dulaiova, Jan Kamenik and Kamila
Stastna
Department of Geology and Geophysics,
University of Hawaii, Honolulu, HI 96822
E-mail: hdulaiov@hawaii.edu
It has been
one year since the great Tohoku earthquake and subsequent tsunami on March 11,
2011. These events resulted in power failures that prevented proper cooling of
several reactors at the Fukushima Daichi nuclear
power plant. Three units experienced partial core meltdown and four had
hydrogen explosions that damaged the reactor containments. Significant amounts
of radionuclides were released to the atmosphere and by direct discharge or leakage
to the ocean. It is estimated that over the couple of weeks after the
accident 1 to 4 x1016 Bq cesium-137 was
released to the environment making it the second largest accidental release of
radioactivity after Chernobyl (http://www.sciencedirect.com/science/article/pii/S0265931X1100289X).
For
atmospheric releases it was only a matter of days before they dispersed in the
northern hemisphere. Fukushima-related radionuclides in the atmosphere were
registered by air- and rainwater monitoring systems (RadNet,
epa.gov) across the US, in particular in Alaska, California, Guam, Hawaii,
Idaho, Nevada, Saipan, Northern Mariana Islands, Washington and even on the
east coast in Massachusetts and Pennsylvania. As early as on March 22, 2011 the
US Environmental Protection Agency reported that
" As of 6:30pm (EDT) preliminary monitor results in Hawaii detected
minuscule levels of an isotope that is consistent with the Japanese nuclear
incident. This detection varies from background and historical data in
Hawaii." (www.epa.gov/japan2011).
Figure
1, left panel: EPAÕs RadNet monitoring network does
regular year-round gross beta radiation measurements on air filters in Hilo and
Honolulu (http://www.epa.gov/narel/radnet/). An increase in beta activity was observed in Guam, the
Commonwealth of Northern Marianna Islands and Hawaii after the Fukushima
accident. Right panel: CNMI and Guam observed half as large increase in gross
beta radiation than the station in Kahuku, HI. The
windward side of Oahu (Kahuku) had nine times the
increase in beta radiation than the leeward side (Honolulu). The EPA also
deployed samplers to analyze specific radionuclides and found 137Cs,
134Cs, 132Te, 132I and 131I, which
are indicative of Fukushima releases. Table 1 shows the maximum detected levels
of cesium for some of the Pacific Islands. These radiation levels do not pose a
health risk for the US population.
Most
of atmospheric releases were blown towards the Pacific Ocean rather than
depositing on Japan but experts are still working on estimating how much of
radiation was released and deposited on land and in the ocean.
Our
group at the Department of Geology and Geophysics, University of Hawaii in Manoa started monitoring seawater radiocesium
(134Cs and 137Cs) concentrations immediately after the
accident. We have been collecting samples at Waikiki and the HOT cruise graciously
provided us monthly water samples from the offshore station Aloha (http://hahana.soest.hawaii.edu/hot/) starting April 2011. So far no
Fukushima related radiation has been found in the ocean at these two locations.
In
addition we received samples from Guam collected by colleagues at the
University of Guam and the Midway Islands that were collected by a SEA education
cruise (http://www.sea.edu/?gclid=COj-yKys4K4CFWMGRQodXGb9ZQ) in March and April,
2011. These samples would indicate radiation from atmospheric fallout since it
was too early for the ocean releases to travel that far, though no Fukushima
radiation was detected.
We can say
that no Fukushima related radiation was found, but there is plenty of radioactivity in the ocean from both natural and man-made
sources. Cesium isotopes are produced in nuclear reactors and have radioactive
half-lives 137Cs = 30 years and 134Cs = 2 years. Cesium
behaves chemically very similarly to potassium, it is a conservative element
that attaches to particles very little and does not take part in any major
chemical reactions in the surface ocean. This element therefore works best as a
tracer of Fukushima releases because it stays dissolved in the ocean water and
is carried by currents. As opposed to other elements such as actinides
(plutonium, americium) that attach to particles (plankton, dust) and are readily
removed from the surface ocean by settling.
Based
on results collected in the International Atomic Energy AgencyÕs MARIS database
the Central Pacific had pre-Fukushima 137Cs activities of about 1.2
- 1.4 Bq/m3. This is leftover after nuclear
weaponsÕ testing and the Chernobyl accident. The half-life of this isotope is
30 years so it stays around for a couple of decades after its release. 134Cs
on the other hand, has a half-life of 2 years and in about 5 half-lives so 10
years 97% of it decays. Fukushima releases had both of these in a ratio of 1:1.
Our methods can detect as little as 0.2 Bq/m3
of cesium, so in every sample we could see 1.2-1.5 Bq/m3
137Cs, but no detectable 134Cs.
To put
these activities in perspective, we can compare the cesium to naturally
occurring potassium, which has a radioactive isotope 40K. Its
activity in seawater is 11,000 Bq/m3. In
some parts of the ocean near Japan activities approached this level, but not
around Hawaii.
People
in Hawaii are also concerned about the potential contamination of the debris
released by the tsunami. It is hard to track the debris field in the ocean (http://www.oceanrecov.org/tsunami-debris/maps.html) and
certainly it is beyond our means to survey it all for radioactivity. While it
is possible that atmospheric fallout impacted some of the debris, the largest
releases of radioactive waters to the ocean happened the first week of April, 2011 after the debris has mostly moved offshore.
We participated on a scientific cruise organized by
scientists from the Woods Hole Oceanographic Institution funded by the Moore
foundation. The University of Hawaii research vessel R/V Kaimikai-O-Kanaloa was used
to sail between Yokohama, Japan and 147 degrees longitude east along the northern
side of the Kuroshio current
(http://www.whoi.edu/page.do?pid=67796). On the way
back to Hawaii surface water samples were collected (black dots and red crosses
on the maps below) which we then analyzed for 137Cs and134Cs. The cruise
track intersected the southern edge of the modeled debris field (bottom panel
of figure 2). While we found Fukushima related radionuclides, the levels were
rather low (< 12 Bq/m3 of each isotope).
However, we know based on results from other researchers that in some places
radioactivity was much higher, about 1,000 times the
normal. We did not have a chance to measure the radioactivity of the debris.
Figure 2: Map
of sampling locations in the East and Central Pacific Ocean. The Fukushima-
Honolulu transect was sampled in June 2011, Guam and Midway in March and April, 2011. Coastal Oahu and station Aloha have been
sampled since late March. 20-100 L of surface water is collected and processed
through an AMP-PAN resin, which selectively sorbs cesium. The resin is then
counted by gamma-spectrometry for 137Cs & 134Cs. The
chemical recovery is determined using stable cesium via ICP-MS analysis.
The bottom
panel shows the modeled tsunami debris field by Nikolai Maximenko
and Jan Hafner from the University of Hawaii International
Pacific Research Center (http://www.soest.hawaii.edu/iprc/news/marine_and_tsunami_debris/debris_news.php).
This material is based
upon work supported by NSF under grant No. RAPID OCE-1137412,
the Gordon and Betty Moore Foundation and the School of Ocean Earth Science and
Technology, UH. Any
opinions, findings, and conclusions or recommendations expressed in this
material are those of the authors and do not necessarily reflect the views of
the funding agencies.