1973
DOI: 10.2172/4563099
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In-situ measurement of radionuclides in the environment with a Ge(Li) spectrometer.

Abstract: tWi l» • artafiat at a paatr IMaaati far aafrllttilaa to • Marital ar •rieiiilMi. Mae* dM«f>a Buy hi atari* (Miar* •*!*««•*, tla* jH»arIai I* MM* available aftitt ^^sa^^as^-7151^ 8ECE1VED BY T'C I,'..

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Cited by 10 publications
(4 citation statements)
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“…al.., 1973), but a longer half-time of decrease of about 10 weeks vas observed by Anspaugh, et al. (1973) during one experiment conducted 12 to ho veeks post re lease ar-i Sehmel and Orgill (197't) reported a half-time of about 9 months after a 10 year old source had been artificially disturbed; 3) Such long-term decreases of the concentration of resuspended radionuclides with time are not due to an appreciable net loss of radionuclide from the area, but to a "weathering" process whereby the contaminant becomes less erodible (Shreve, 1958;Olafson and Larson, 1961;Stewart, 196U;Larson, et_ aj^., 1966); k) Areas which were contaminated 10 to 20 years previously are still significant sources of resuspended radioactive par ticulates {Anspaugh, et a^.…”
Section: Radionuclide Resuspension Studiesmentioning
confidence: 85%
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“…al.., 1973), but a longer half-time of decrease of about 10 weeks vas observed by Anspaugh, et al. (1973) during one experiment conducted 12 to ho veeks post re lease ar-i Sehmel and Orgill (197't) reported a half-time of about 9 months after a 10 year old source had been artificially disturbed; 3) Such long-term decreases of the concentration of resuspended radionuclides with time are not due to an appreciable net loss of radionuclide from the area, but to a "weathering" process whereby the contaminant becomes less erodible (Shreve, 1958;Olafson and Larson, 1961;Stewart, 196U;Larson, et_ aj^., 1966); k) Areas which were contaminated 10 to 20 years previously are still significant sources of resuspended radioactive par ticulates {Anspaugh, et a^.…”
Section: Radionuclide Resuspension Studiesmentioning
confidence: 85%
“…, 197trt>;197'tc;Sehmel and Orgill, 19714); 5) For explosion-produced sources, the quotient of j.ir concentration of resuspended contaminant divided by ground deposition increases with dis tance from the source (Wilson, et al, I960;Larson, et al, 1966;Anspaugh, et_ al., 1971) which may be partly due to the decrease in par ticle size of the contaminant which is deposited at further distances (Shreve, 1958); 6) Short-term, order of magnitude fluctuations of the airborne concentration of resuspended radionuclides are frequently observed presumably due to changes in meteorological conditions although functional relationships are not well-defined, especially for freshly deposited sources (Shreve, 1958;Wilson, et. al., ?960;Olafson and Larson, 196l;Larson, et al, 1966;Anspaugh, et al_., 1973); 7) Arti ficial disturbances in a contaminated environment can also produce orders of magnitude increases in the airborne concentration of contaminant (Mork, 1970;Sehmel, 1973;Sehmel and Orgill, 197't); and 8) Measurements of the particle size distributions of resuspended, plutonium-containina: aerosols indicate that the fraction which vould undergo pulmonary depo sition is about 0.15 to 0.25 (Wilson, et <a., I960;Volchok and Knuth, 1972;Anspaugh, et_ al., 197i»o).…”
Section: Radionuclide Resuspension Studiesmentioning
confidence: 99%
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“…Although this must ultimately be determined based on specific local conditions, it appears to be a reasonable assumption for purposes of this methodology. Several researchers have measured gamma emitters in soil that reasonably confirm this assumption beyond the radon gas decay products (Anspaugh et al 1972;Bolch et al 1976). The specific activity of some I' Depending on site specific conditions, soil specific activities could vary by a factor of about 0.5 to 5 times these assumed values.…”
Section: Activitymentioning
confidence: 90%