http://news.softpedia.com/news/
Chernobyl Still Radioactive After 23 Years
Even more so than originally expected
The Chernobyl nuclear power plant after the meltdown, showing reactor
4 with its roof blown off
Speaking at the annual meeting of the American
Geophysical Union (AGU) on Monday, experts revealed a troublesome fact
about Chernobyl, the Ukrainian nuclear power plant that blew up in 1986.
Recent measurements in the exclusion zone, where no humans can go without
protective equipment, have revealed that the radioactive material that
was spilled in the area was nowhere near the decay level that was predicted
for it. In other words, the scientists are saying that it will take a lot
more time for the land to be cleansed than originally believed, Wired
reports.
Previous estimates, based on the fact that
the Cesium 137's half-life is 30 years, estimated that the restriction
zone could be lifted, and then re-inhabited soon. But experiments reveal
that the radioactive material is not decaying as fast as predicted, and
scientists have no clue as to why this is happening. The April 26, 1986
accident was the largest nuclear accident in the world, and only a level
7 event on the International Nuclear Event Scale. Its fallout was made
worse by the Soviet Union's attempt at covering up the incident, which
saw a lot of people exposed to lethal doses of radiations.
"Normally you'd say that every 30 years,
it's half as bad as it was. But it's not. It's going to be longer before
they repopulate the area," Savannah River National Laboratory nuclear
scientist Tim Jannick, who has also collaborated in the new investigation,
said at the AGU conference. The new estimates point out that the half-life
for ecological Cesium 137, the variety out in the open, is between 180
and 320 years. This pours a stream of cold water on the Ukrainian authorities'
plans to start reusing the land.
"I have been involved in Chernobyl studies
for many years and this particular study could be of great importance to
many [Department of Energy] researchers," Lawrence Berkeley National
Laboratory (Berkeley Lab) nuclear remediation expert Boris Faybishenko
says. In the greater scheme of things, the fallout and nuclear disaster
provided researchers with a window of opportunity into studying the possible
effects of radiation poisoning on the environment and ecosystems. For the
past 20 years, teams have been analyzing how strontium, plutonium and cesium
isotopes infiltrate the ground around Chernobyl several times annually.
http://www.wired.com/
Chernobyl Exclusion Zone Radioactive Longer Than Expected
SAN FRANCISCO — Chernobyl, the worst nuclear accident in history, created
an inadvertent laboratory to study the impacts of radiation — and more
than twenty years later, the site still holds surprises.
Reinhabiting the large dead zone around the
accident site may have to wait longer than expected. Radioactive cesium
isn't disappearing from the environment as quickly as predicted, according
to new research presented here Monday at the meeting of the American Geophysical
Union. Cesium 137's half-life — the time it takes for half of a given amount
of material to decay — is 30 years, but the amount of cesium in soil near
Chernobyl isn't decreasing nearly that fast. And scientists don't know
why.
It stands to reason that at some point the
Ukrainian government would like to be able to use that land again, but
the scientists have calculated that what they call cesium's "ecological
half-life" — the time for half the cesium to disappear from the local environment
— is between 180 and 320 years.
"Normally you'd say that every 30 years,
it's half as bad as it was. But it's not," said Tim Jannick, nuclear
scientist at Savannah River National Laboratory and a collaborator on the
work. "It's going to be longer before they repopulate the area."
In 1986, after the Chernobyl accident, a series
of test sites was established along paths that scientists expected the
fallout to take. Soil samples were taken at different depths to gauge how
the radioactive isotopes of strontium, cesium and plutonium migrated in
the ground. They've been taking these measurements for more than 20 years,
providing a unique experiment in the long-term environmental repercussions
of a near worst-case nuclear accident.
|
suite:
In some ways, Chernobyl is easier to understand
than DOE sites like Hanford, which have been contaminated by long-term
processes. With Chernobyl, said Boris Faybishenko, a nuclear remediation
expert at Lawrence Berkeley National Laboratory, we have a definite date
at which the contamination began and a series of measurements carried out
from that time to today.
"I have been involved in Chernobyl studies
for many years and this particular study could be of great importance to
many [Department of Energy] researchers," said Faybishenko.
The results of this study came as a surprise.
Scientists expected the ecological half-lives of radioactive isotopes to
be shorter than their physical half-life as natural dispersion helped reduce
the amount of material in any given soil sample. For strontium, that idea
has held up. But for cesium the the opposite appears to be true.
The physical properties of cesium haven't
changed, so scientists think there must be an environmental explanation.
It could be that new cesium is blowing over the soil sites from closer
to the Chernobyl site. Or perhaps cesium is migrating up through the soil
from deeper in the ground. Jannik hopes more research will uncover the
truth.
"There are a lot of unknowns that are probably
causing this phenomenon," he said.
Beyond the societal impacts of the study,
the work also emphasizes the uncertainties associated with radioactive
contamination. Thankfully, Chernobyl-scale accidents have been rare, but
that also means there is a paucity of places to study how radioactive contamination
really behaves in the wild.
"The data from Chernobyl can be used for
validating models," said Faybishenko. "This is the most value that
we can gain from it."
Citation: "Long-Term Dynamics of Radionuclides Vertical Migration in
Soils of the Chernobyl Nuclear Power Plant Exclusion Zone" by Yu.A. Ivanov,
V.A. Kashparov, S.E. Levchuk, Yu.V. Khomutinin, M.D. Bondarkov, A.M. Maximenko,
E.B. Farfan, G.T. Jannik, and J.C. Marra. AGU 2009 poster session.
Voir aussi :
http://www.sciencedirect.com/
doi:10.1016/j.jenvrad.2008.10.010
Vertical migration of radionuclides in undisturbed
grassland soils
Gerald Kirchnera, Friederike Streblb, Corresponding
Author Contact Information, E-mail The Corresponding Author, Peter Bossewc,
Sabine Ehlkend and Martin H. Gerzabeke
a) BfS Federal Office for Radiation Protection, D-38201 Salzgitter,
Germany
b) Austrian Research Centers GmbH (ARC), Department of Radiation Safety
and Applications, A-2444 Seibersdorf, Austria
c) Institute for Environment and Sustainability, DG Joint Research
Centre, European Commission, I-21020 Ispra, Italy
d) Klinikum Bremen-Mitte, D-28177 Bremen, Germany
e) University of Natural Resources and Applied Life Sciences Vienna,
Peter-Jordan-Strasse 82b, A-1190 Vienna, Austria
Abstract
Literature data on numerical values obtained
for the parameters of the two most popular models for simulating the migration
of radionuclides in undisturbed soils have been compiled and evaluated
statistically. Due to restrictions on the applicability of compartmental
models, the convection–dispersion equation and its parameter values should
be preferred. For radiocaesium, recommended values are derived for its
effective convection velocity and dispersion coefficient. Data deficiencies
still exist for radionuclides other than caesium and for soils of non-temperate
environments.
1. Introduction
2. Models
for the transport of radionuclides in soils
2.1. Compartmental
models
2.2. Convection–dispersion
models
2.3. Links
between Kd-values and migration parameters
3. Parameters
for vertical migration in undisturbed soil profiles
3.1. Time
dependence of 137Cs vertical migration
3.2. Effect
of soil texture on 137Cs migration
3.3. Migration
rates of 137Cs in different contamination scenarios
3.4. Influence
of fuel hot particles on migration rates in soil
3.5. Vertical
migration of radionuclides other than 137Cs
4. Conclusions
References |