radiocesium concentration in milk after the chernobyl accident in japan
TRANSCRIPT
J.RADIOANAL.NUCL.CHEM~ 145 /2[ 151-157 [1990/ J
RADIOCESIUM CONCENTRATION IN MILK AFTER THE CHERNOBYL ACCIDENT IN JAPAN
T. Imanaka, H. Koide
Research Reactor Institute, Kyoto University, Kumatori-cho, Sennan-gun, Osaka 590-04, Japan
Received 19 March 1990 Accepted 27 March 1990
Radiocesium concentrations in cow's milk from two producing districts in Japan were measured monthly for three years following the Cherno- bvl accident. The Chernobyl contribution in ~Cs Concentration was evaluated f~om the lJaCs concentration and the 137Cs/l~4Cs ratio. The highest 137Cs concentration of 0.6 Bq 1 -I was observed in May 1986 and the Chernobyl contribution has decreased during three years to levels corresponding to the contribution from past nuclear weapons fallout. Annual values of child internal dose through milk consumption were estimated at 0.6, 0.3 and O.i uSv for the first, the second and the third year following the accident, respective- ly.
INTRODUCTION
The Chernobyl accident in April 1986 caused widespread
radioactivity contamination throughout the northern hemi-
sphere. Radioactive plumes arrived in Japan on 3 May,
twenty kinds of y-emitting nuclidebeing identified in 1
air . Among the nuclides released from the Chernobyl re-
15 | E~evier Sequom S. A., L~sanne A k ~ m m i Ki~6, B ~ e s t
IMANAKA, KOIDE: RADIOCESIUM IN MILK AFTER CHERNOBYL ACCIDENT IN JAPAN
actor, two cesium isotopes, 137Cs and !34Cs are most im-
portant to evaluate the long-term radiological effect of
the accident 2'3. The average value of the 137Cs deposition
in Japan is estimated to be 180 Bq.m -2 /Ref. 3/. Although
the contamination level in Japan were not as serious as
those in European countries, radioactivity contamination
has also become a matter of public concern.
~e commenced the monthly measurement of radioactivity in
cow's milk from two producing districts in Japan just af-
ter the accident. This paper presents the results of our
measurement for three years following the accident.
MATERIALS AND METHODS
Samples of commercial milk were collected monthly throus
dairy co-operatives in two milk producing districts: Toka-
chi, plain fields in the Hokkaido island and Hiba, a moun-
tainous district in Hiroshima prefecture in the Honsyu
island /Fig. i/. Tokachi is a district where large-scale
dairy farming is extensively carried on. In Hiba, however,
dairy farming with large meadowland is not available and
hence imported crops are fed to dairy cows to cover the
shortage of local fodder.
Milk samples before December 198~ were measured in a
l-litre Marinelli beaker without any pretreatment. There-
after milk samples of one or two litre were dried under
infrared lamps and reduced to ashes in an electric fur-
nace at about 450 ~ to concentrate nuclides before the
activity measurement.
Gamma-ray spectra from liquid milk or milk ashes were
obtained with an intrinsic Ge detector /relative efficien-
cy 19%, resolution 1.8 keV at !.33 MeV/. The detector was
connected to a 4k channel analyzer and shielded from room
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IMANAKA, KOIDE: RADIOCESIUM IN MILK AFTER CHERNOBYL ACCIDENT IN JAPAN
_...... &&~
1.5.
~onsyu Is.
pacific ,OceOr~
~ o
132 ~ 136 ~
Fig. i. Location of milk producing districts; Tokachi and Hiba
background with iO cm of lead. Efficiency calibration for
each geometry was carried out with a CEA standard solution
of mixed nuclides. Counting times ranged from about one
day for initial samples to more than four days for later
samples. Detection limits of radiocesium activity are
about 0.04 and O.O1 Bq.l -I for liquid milk and milk ashes,
respectively.
RESULTS AND DISCUSSION
Radioactivity in milk
The radiocesium concentration in milk obtained from
May 1986 through April 1989 is shown in Fig. 2, all values
being decay-corrected to the date of milk production.
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IMANAKA, KOIDE: RADIOCESIUM IN MILK AFTER CHERNOBYL ACCIDENT IN JAPAN
1 ! , j .
I 7 0 i I I I I I I I I 1 1 I I I I I 1 1
Fig. 2. Concentration trends of ra~iocesium in cow's milk from May 1986 to April 1989: 137Cs in Tokachi / ~. /, 134Cs in Tokachi / O/, 137Cs in Hiba / m / and 134Cs in Hiba / ~ /. Bars indicate the standard er- ror
At the time of the fallout arrival, the beginning of
May 1986, it was already in season of fresh green in Hiba
but was not yet in Tokachi. Thus, at the early stage of
the contamination, cows in Hiba had more chance of grazing
contaminated pasture than those in Tokachi, which led to
higher values of radiocesium concentration in the former
district. The highest 137Cs concentration in Hiba milk,
0.6 Bq.l -I, was observed in May 1986, while in Tokachi
milk the highest concentration, 0.4 Bq.l -I, was in July
1986. We also detected 131I activiEy in initial samples,
but the concentration decreased below the detectable limit
withintwo months; maximum concentrations were 2.6 and
0.9 Bq.l -I in Hiba and Tokachi, respectively.
After the first half-year, however, radiocesium con-
centration in Tokachi milk was consistently higher than
154
IMANAKA, KOIDE: RADIOCESIUM IN MILK AFTER CHERNOBYL ACCIDENT IN JAPAN
in Hiba milk /except in April 1987 when a significant
increase was observed in Hiba/. This trend may be explained
with the difference in the feed contents; the major part
/about 50 wt%/ of feed is a blend of imported crops /most-
ly from the United States/ in Hiba, while in Tokachi suf-
ficient pasture areas are available locally.
Time-integrated concentration
Since the 137Cs avtivity includes the contribution
from past nuclear weapons tests, it is necessary to know
the Chernobyl contribution in 137Cs concentration for
the evaluation of the effect of the accident. The activi-
ty ratio of 137Cs to 134Cs fromChernobyl was 2.0 at the
time of the fallout arrival in Japan I'4. Therefore, the
Chernobyl contribution in 137Cs concentration was obtained
by multiplying the 134Cs concentration by the 137Cs/134Cs ratio, wfth the decay correction of the difference in
their half-lives.
Table 1 summarizes values of time-integrated concentra-
tion observed during each year following the accident; va-
lues in Hiba for the third year /May 1988 to April 1989/
were obtained by extrapolating the preceding values since
134Cs activity in Hiba milk decreased below the detectable
limit of the measurement by the summer of 1988. As shown
in Table i, the Chernobyl contribution in 137Cs concentra-
tion decreased during three years to levels corresponding
to the contribution from past nuclear weapons fallout.
Internal dos E from milk consumption
The estimation of internal dose due to Chernobyl-de-
rived 137Cs and 134Cs was made for a childrwho had been
consuming Tokachi milk after the accident. A milk consumption
rate of 0.5 1 d -I and dose conversion factors of 0.0086
uSv. Bq -I for 137Cs and 0.O12 uSv. Bq -I for 134Cs were as-
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IMANAIC&, KOIDE: RADIOCESIUM IN MILK AFTER CHERNOBYL ACCIDENT 1N JAPAN
TABLE 1
Time-integrated radiocesium concentrations in milk during each year following the accident; contribution from
Chernobyl and past weapons tests. /Bq.y-l-i/
Chernobyl
District and period 134Cs 137Cs
Weapons tests
137Cs
Tokachi:
May 1986-April 1987
May 1987-April 1988
May 1988-April 1989
Hiba:
May 1986-April 1987
May 1987-April 1988
May 1988-April 1989
O.10+0.O3 0.24+0.07 0.06+0.05
0.04+0.02 0.12+O.06 0.07+0.02
0.02+0.O1 0.07+0.02 0.07+0.03
O.13+0.10 0.28+0.20
0.02+0.O1 0.05+0.02
O.005 x 0.02 ~
0.04+0.03
0.02+0.02
0.02 ~
XEstimated by extrapolating s preceding values.
sumed in accordance with the recommendation by Japan Nuc-
lear Safety Committee 5. Thus annual values of effective
dose equivalent were estimated to be 0.6, 0.3 and 0.i
uSv for the first, the second and the third year following
the accident, respectively.
x
Thanks are due to staffs of Kansai-Yotsuba Co-operative
for providing us with milk samples and to Mr. K. Ii, the
chief director of the dairy farming co-operative in Hiba,
with kindly information on their dairy farming.
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IMANAKA, KOIDE: RADIOCESIUM IN MILK AFTER CHERNOBYL ACCIDENT IN JAPAN
REFERENCES
i. T. Imanaka, H. Koide, J. Environ. Radioact., 4 /1986/ 149.
2. The Radiobiological Impact of the Chernobyl Accident in OECD Countries, OECD/NEA, Paris, 1987.
3. Sources, Effects and Risks of Ionizing Radiation, UNSCEAR, New York, 1988.
4. M. Aoyama, K. Hirose, Y. Suzuki, H. Inoue, Y. Sugimura, Nature, 321 /1986/ 819.
5. Japan Nuclear Safety Committee, Gensiryoku Anzen Iinkai Geppou 126, 1989.
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