“…Howard et al (1993) reported an F m value of 2.9 Â 10 À1 d L À1 based on a controlled experiment with measured intakes of Chernobyl-contaminated herbage. Data from Bustad et al (1957) were used by Howard et al (1993) to derive an F m value of 3 Â 10 À1 d L À1 ; Howard et al (1993) also quote a value of 5.6 Â 10 À1 d L À1 derived from stable iodine measurements. Data not considered in TRS 364 include an F m value derived using a model based analysis of Chernobyl related field based measurements of 1.0 Â 10 À1 d L À1 (Monte, 1990) and an F m value of 7.0 Â 10 À2 d L À1 which we derived from field measurements by Hanušík et al (1997).…”
Section: Radionuclide Transfer To Sheep Milkmentioning
An overview of original information available from Russian language papers on radionuclide transfer to milk is provided. Most of the data presented have not been taken into account in international reviews. The transfer coefficient (F(m)) values for radioactive isotopes of strontium, caesium and iodine are in good agreement with those previously published. The Russian language data, often based on experiments with many animals, constitute a considerable increase to the available data for many less well-studied radionuclides. In some instances, the Russian language data suggest changes in recommended values (e.g. Zr and Ru). The information presented here substantially increases the amount of available data on radionuclide transfer to milk and will be included in the current revision of the IAEA TRS Handbook of parameter values for radionuclide transfer.
“…Howard et al (1993) reported an F m value of 2.9 Â 10 À1 d L À1 based on a controlled experiment with measured intakes of Chernobyl-contaminated herbage. Data from Bustad et al (1957) were used by Howard et al (1993) to derive an F m value of 3 Â 10 À1 d L À1 ; Howard et al (1993) also quote a value of 5.6 Â 10 À1 d L À1 derived from stable iodine measurements. Data not considered in TRS 364 include an F m value derived using a model based analysis of Chernobyl related field based measurements of 1.0 Â 10 À1 d L À1 (Monte, 1990) and an F m value of 7.0 Â 10 À2 d L À1 which we derived from field measurements by Hanušík et al (1997).…”
Section: Radionuclide Transfer To Sheep Milkmentioning
An overview of original information available from Russian language papers on radionuclide transfer to milk is provided. Most of the data presented have not been taken into account in international reviews. The transfer coefficient (F(m)) values for radioactive isotopes of strontium, caesium and iodine are in good agreement with those previously published. The Russian language data, often based on experiments with many animals, constitute a considerable increase to the available data for many less well-studied radionuclides. In some instances, the Russian language data suggest changes in recommended values (e.g. Zr and Ru). The information presented here substantially increases the amount of available data on radionuclide transfer to milk and will be included in the current revision of the IAEA TRS Handbook of parameter values for radionuclide transfer.
“…(5) Sheep fed 240 pc or 1.8 mc daily exhibited early mean concentration ratios of 2.4 and 2.2, as compared with 3-7 for animals fed 0.15 pc daily. The effective half-life of Il3I in the thyroids of sheep given 15 mc showed an abrupt transition from 6.5 days to 1.7 daydll) at 4-5 days after administration.…”
“…The Public Health Service (PHS) and Atomic Energy Commission (AEC) at the time corroborated these findings but downplayed the risks (Flemming, 1959(Flemming, , 1960Wolff, 1957Wolff, , 1959. The scientific literature from the period also suggests that fallout exposure may adversely affect agricultural production (Bustad et al, 1957;Garner, 1963;Sparrow et al, 1971).…”
Section: Biological Effects Of Radiation Poisoningmentioning
confidence: 95%
“…In comparison, the partial nuclear meltdown at Chernobyl released approximately 81 million Curies of radioactive material (LeBaron, 1998). The scientific and medical literature shows that fallout from these domestic tests harmed human and animal populations (Bustad et al, 1957;Garner, 1963;National Cancer Institute, 1997) and it is quite plausible that pollution created from nuclear testing had first order effects upon domestic agriculture.…”
In the 1950s the United States conducted scores of atmospheric nuclear tests at the Nevada Test Site. This article studies the effects of radioactive fallout from nuclear tests on agriculture in regions hundreds of miles from the NTS. While research has shown that this radioactive material posed a health risk near the NTS, little is known about the direct economic effects nuclear testing may have had. I find that fallout from nuclear tests adversely affected U.S. agricultural production, and this result suggests that nuclear testing had a much broader economic and environmental impact than previously thought.
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