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Feeding green-cut forage contaminated by radioactive fallout to dairy cows.

Grass contaminated by radioactive fallout from the Chernobyl accident was cut with 150 mm (Treatment 1) and 50 mm (Treatment 2) stubble height and fed to 20 dairy cows. The transfer of 137Cs and 131I from the greencut forage to milk was studied during a four-week and a two-week period, respectively. The four-week period was followed by a three-week period with nearly uncontaminated feeds. Cutting with high stubble height significantly reduced the activity concentration in forage compared with low stubble cutting, the average contents kg-1 dry matter being 385 Bq 137Cs and 24 Bq 131I in Treatment 1 versus 6656 Bq 137Cs and 249 Bq 131I in Treatment 2. Apparent treatment effects were also demonstrated by the 137Cs concentration in milk, with maximum weekly means of 23 Bq kg-1 (Treatment 1) and 92 Bq kg-1 (Treatment 2). Single day maximum concentrations of 131I in milk were 4 Bq kg-1 (Treatment 1) and 9 Bq kg-1 (Treatment 2). The mean transfer coefficients (d kg-1) were calculated to be 0.67 X 10(-2) and 0.19 X 10(-2) for 137Cs (weeks 2-4) and 1.8 X 10(-2) and 0.2 X 10(-2) for 131I (week 2) in Treatments 1 and 2, respectively. The lower value for 137Cs might possibly be associated with an enhanced ash content of the forage. Feeding nearly uncontaminated rations rapidly decreased the 137Cs levels in milk in both treatments with calculated effective half-times over the three-week period of 10 and 7 d, respectively.

Accidents↗

Cancer incidence in an area of radioactive fallout downwind from the Nevada Test Site.

Exposures in southwestern Utah to radioactive fallout (1951 through 1962) from atmospheric nuclear detonations at the Nevada Test Site (NTS) were followed by smaller exposures (1962 through 1979) from venting of underground nuclear detonations. The cancer incidence in a 1951 cohort (4, 125) of Mormon families in southwestern Utah near the NTS was compared with that of all Utah Mormons (1967 through 1975). There were 109 more cases of cancer than expected (288[observed]/179[expected]). Leukemia was most prominent early (1958 through 1966), with 19 cases, five times more than expected (3.6). The excess of leukemia persisted into the later period (1972 through 1980), with 12 cases observed, 3.4 expected. There was an increase in lymphoma. Excess cases of thyroid cancer appeared early and a notable excess appeared later (14/1.7). An excess of breast cancer was noted later (27/14). There were more cancers of the gastrointestinal tract than expected. There was an excess of melanoma (12/4.5), bone cancer (8/0.7), and brain tumors (9/3.9). A subgroup with history of acute fallout effects had a higher cancer incidence. That these cases can be associated with radiation exposures is supported by a comparison between groups of the ratio of cancers of more radiosensitive organs with all other types of cancer.

Adolescent↗

Studies of radioactivity produced by the Hiroshima atomic bomb: 2. Measurements of fallout radioactivity.

Three studies of fallout measurements were reviewed for the discussion of possible radioactivity intake from the Hiroshima atomic bomb. The first study discussed correlations between enriched 234U and 137Cs specific activities from the measurement of soil samples collected in the "black rain" area. The second study measured 137Cs activity on the rock and roof tile samples collected in the hypocenter area immediately after the explosion. Some of the rock and roof tile samples collected near the hypocenter had a small but detectable amount of 137Cs activity. However, it has been determined that 137Cs exposure, for example, was negligible compared with DS86 dose estimates, since these activity levels were low. The third study detected 90Sr activity in some of the specimens of human bones exhumed on Ninoshima Island. This study compared the difference in activity between the bone head and shaft, with higher activities obtained in the bone head. This fact suggests a short intake period for this activity, however, the levels of 90Sr contamination were too low to allow a discussion of the exposure risks.

Humans↗

Prevalence of thyroid autoantibodies in children and adolescents from Belarus exposed to the Chernobyl radioactive fallout.

BACKGROUND: The long-term effects of ionising radiation, including radioiodine, on thyroid function are not well known. We compared thyroid immunity and function in two groups of children from Belarus, one of whom was exposed to the radioactive fallout of Chernobyl. METHODS: We measured serum free thyroxine 4 (free T4), free T3, and thyrotropin hormone (TSH) and the prevalence of thyroid autoantibodies (antithyroglobulin and antithyroperoxidase), in 287 children or adolescents living in Hoiniki (average caesium contamination of 5.4 Ci/km2). We also studied 208 children and adolescents living in Braslav (average contamination <0.1 Ci/km2), who were age 12 years or less at the time of the Chernobyl accident. FINDINGS: The prevalence of antithyroglobulin or antithyroperoxidase, or both, was significantly higher (p=0.0001) in individuals living in Hoiniki (56 [19.5%] of 287) than in those living in Braslav (eight [3.8%] of 208). In both villages, no sex differences were found in the antibody prevalence before age 13 years. Thereafter, a significantly higher prevalence of thyroid autoantibodies was found in girls from Hoiniki. The increase in the prevalence of circulating antibodies in the contaminated group was already apparent in individuals who, at the time of the accident, were in utero or newborn (15.7%), and was even more pronounced in children of 9 years or more (35.1%). No major alterations of serum FT-4, FT-3, or TSH were found. INTERPRETATION: 6-8 years after the Chernobyl accident, a significant increase in thyroid autoimmunity was found in children exposed to radioactive fallout. Pubertal age in girls is a risk factor for increased prevalence of thyroid autoimmunity. The autoimmune phenomena are limited to an increased prevalence of circulating thyroid autoantibodies without evidence of significant thyroid dysfunction. The future development of clinically relevant thyroid autoimmune diseases, especially hypothyroidism, is a possibility.

Adolescent↗

Radioactive fallout in Norway from atmospheric nuclear weapons tests.

Historical data on radioactivity in air and precipitation samples have been collected and analysed from study sites in Norway. The purpose of the study was to investigate the correlation between air concentration, precipitation and deposition, and identify areas with high deposition. Areas with high precipitation have been compared with monitoring stations in other countries. The base line data contain measurements of total beta in air and precipitation on a daily basis for the period 1956-1982. Radioactive fallout correlated strongly with annual precipitation which varies from 280 to 4200mm per year in Norway. The deposition of 137Cs was calculated to be 3.23+/-1.20kBq/m2 per 1,000 mm precipitation for the period 1955-1975. Also, the relationship between total beta and 137Cs has been investigated, in order to estimate the age of fallout. The age of fallout in Norway ranges from 3 to 9 months during the test periods, which is considerably shorter than the global average, where the mean residence time for debris in the lower stratosphere is estimated to be 1.3 years. There is no evidence of local fallout from tests on Novaya Zemlya reaching Norwegian areas.

Cesium Radioisotopes↗

Effects of radioactive fallout on soil animal populations in the 30 km zone of the Chernobyl atomic power station.

Studies were carried out during July and September 1986, April 1987, and October 1988. Radioactive fallout after the Chernobyl atomic power station (APS) accident induced catastrophic effects on populations of small pine-litter faunae within the 3 km zone around the station. Effects on soil faunae were not so marked due to shielding by the soil, or on litter faunae at the edge of the 30 km zone due to distance from the source. Thirty-gray doses did not directly affect adult animals in the soil and litter, but impacted their eggs and juveniles. Resident populations recovered slowly during the first year after the accident. Insect migration into the contaminated area was the primary source of soil animal population recovery. After 2-2.5 years, marked differences between populations in the contaminated and control areas were no longer found.

Accidents↗