Patty's Industrial Hygiene, Physical and Biological Agents. Группа авторов
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Название: Patty's Industrial Hygiene, Physical and Biological Agents

Автор: Группа авторов

Издательство: John Wiley & Sons Limited

Жанр: Химия

Серия:

isbn: 9781119816225

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      However, because the radioactive lead is not continuously dispersed throughout the air, but is randomly distributed as a very small number of discrete particles, we must consider the probability of catching a particle in our sample. If one wishes to detect 50% of a DAC, or 4 particles m−3 within ±25% at the 95% CI (confidence interval), the required sample size is 16 m3, calculated as follows:

      According to Poisson statistics

      A bioassay program internally monitors the deposited radionuclides. Two different, complementary bioassay techniques are employed to determine the internally deposited radioactivity. In vivo bioassay means direct determination of internal radionuclides by scanning the whole body, or a selected part of the body, with a sensitive detector. This method is useful only for gamma‐emitting radionuclides or high‐energy beta emitters that generate bremsstrahlung within the body. In vitro bioassay involves the analysis of body fluids, excreta, and exhaled air for the purpose of estimating the original intake. Although a single measurement may suffice for determining whether or not radioactivity is present in the body, generally, repeated measurements are necessary if one wishes to achieve the best estimate of the intake and of the dose.

      The rationale underlying the practice of in vitro bioassay is that a quantitative relationship exists among inhalation or ingestion of a radionuclide, the resulting body burden, and the rate at which the radionuclide is eliminated. From measurements of radioactivity in urine or feces, therefore, one should be able to infer the body burden, and thus estimate the radiation dose. Unfortunately, the kinetics of metabolism in any particular person is influenced by many factors, resulting in a great deal of uncertainty about the exact quantitative relationships among elimination rates, body burden, and radiation dose. In most instances, therefore, bioassay data allows only a reasonable estimate of the intake and dose.

      1 “No radiation‐related deaths or acute diseases have been observed among the workers and general public exposed to radiation from the accident.”

      2 “No discernible increased incidence of radiation‐related health effects are expected among exposed members of the public or their descendants.”

      3 “The most important health effect is on mental and social well‐being, related to the enormous impact of the earthquake, tsunami and nuclear accident, and the fear and stigma related to the perceived risk of exposure to ionizing radiation.”

      4 “Exposures of both marine and terrestrial non‐human biota following the accident were, in general, too low for acute effects to be observed, though there may have been some exceptions because of local variability…”

      More is known about radiation bioeffects than is known for most other environmental stressing agents. Coincident with the expansion of knowledge about radiation bioeffects was the development of sensitive radiation measuring instruments that enabled us to accurately measure radiation fields and quantities of radioactive materials at a level far below that at which harmful radiation effects are seen. This vast amount of dose–response data enables health physicists and industrial hygienists to control the radiation environment in the workplace so that no harmful radiation effects are seen. Thus, medical, scientific, and industrial applications of radiation technology continue at levels of risk no greater than, and often less than, those associated with other applications of science and technology that are generally considered by society to be safe.

      Note

      ENDNOTES

      1 1. Johnson, T.E. and Birky, B.K. (2011). Health Physics and Radiological Health, 4e. New York, NY: Lippincott Williams & Wilkins.

      2 2. Johnson, T.E. (2017). Introduction to Health Physics, 5e. New York: McGraw Hill.

      3 3. Upton, C. (1985). Nonstochastic effects of ionizing radiation, NCRP Proceedings No. 6, Bethesda, MD: National Council on Radiation Protection and Measurements.

      4 4. International Atomic Energy Agency (IAEA) (1994). International Basic Safety Standards for Protection against Ionizing Radiation and for the Safety of Radiation Sources, Safety Series No. 115‐1, Vienna.

      5 5. International Commission on Radiological Protection (ICRP) (1977). Recommendations of the International Commission on Radiological Protection, ICRP Publication 26. Ann ICRP 1 (3).

      6 6. International Commission on Radiological Protection СКАЧАТЬ