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Introduction to Health Physics: Fourth Edition - Ruang Baca FMIPA UB

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BIOLOGICAL BASIS FOR R ADIATION SAFETY 333<br />

Generally, radiation bioeffects fall in<strong>to</strong> one of two categories: deterministic effects<br />

and s<strong>to</strong>chastic effects. Deterministic effects result from exposure <strong>to</strong> very large doses<br />

of radiation. These effects have a threshold dose and their severity increases with<br />

increasing dose. Examples are the acute radiation syndromes that have a threshold<br />

in the range of 1–2 Gy (100–200 rads) whole-body X- or gamma radiation, skin burns<br />

in the range of 2–3 Gy (200–300 rads), and skin ulceration in the range of 20 Gy<br />

(2000 rads). The LD50/60-day dose for whole-body X- or gamma radiation is believed<br />

<strong>to</strong> lie in the range of 3–4 Gy (300–400 rads). Deterministic effects are clearly and<br />

unequivocally causally associated with the radiation exposure.<br />

S<strong>to</strong>chastic effects occur by chance and are seen in unexposed individuals as well<br />

as in exposed individuals and therefore are not unequivocally associated with a radiation<br />

exposure. S<strong>to</strong>chastic effects include cancer and genetic mutations. Exposure <strong>to</strong><br />

radiation increases the probability of a s<strong>to</strong>chastic effect, and this probability increases<br />

with increasing dose. Whereas increased incidence of cancer has been documented<br />

among certain heavily exposed populations—such as the early radiologists, a<strong>to</strong>mic<br />

bomb survivors, and patients who had received radiotherapy—no increased incidence<br />

of heritable changes has ever been observed among any human population<br />

exposed at any dose.<br />

The s<strong>to</strong>chastic effects, either in humans or in animals, that have been observed are<br />

no different in kind from those observed in unirradiated populations. The difference<br />

lies only in the frequency of occurrence. Thus, it is impossible for even the most<br />

highly skilled pathologist <strong>to</strong> definitely attribute any cancer in an exposed individual<br />

<strong>to</strong> the exposure. The only thing that can be done is <strong>to</strong> estimate the probability—<br />

based on the patient’s exposure his<strong>to</strong>ry—that the cancer can be attributed <strong>to</strong> the<br />

radiation exposure. Of the several possible models that have been postulated <strong>to</strong> infer<br />

the s<strong>to</strong>chastic effects of low doses from high-dose cases, the zero-threshold, linear<br />

dose–response relationship, because it is believed <strong>to</strong> be the most conservative of all<br />

the proposed models, was chosen as the basis for setting radiation safety standards.<br />

This brief overview shows that we know enough about the biomedical effects<br />

of radiation <strong>to</strong> enable us <strong>to</strong> set radiation safety standards with a very high level<br />

of confidence that adherence <strong>to</strong> these safety standards will allow the safe use of<br />

radiation and its sources.<br />

SUGGESTED READINGS<br />

Annals of the ICRP. Pergamon, Elsevier Science, Oxford, U.K.<br />

No. 26. Recommendations of the International Commission on Radiological Protection, 1:(3), 1977.<br />

No. 31. Biological Effects of Inhaled Radionuclides, 4:(1/2), 1979.<br />

No. 41. Nons<strong>to</strong>chastic Effects of Ionizing Radiation, 14:(3), 1984.<br />

No. 42. A Compilation of the Major Concepts and Quantities in Use by the ICRP, 14:(4), 1984.<br />

No. 48. The Metabolism of Plu<strong>to</strong>nium and Related Elements, 16:(2/3), 1986.<br />

No. 49. Developmental Effects of Irradiation on the Brain of the Embryo and Fetus, 16:(4), 1986.<br />

No. 50. Lung Cancer Risk from Indoor Exposures <strong>to</strong> Radon Daughters, 17:(1), 1986.<br />

No. 59. The Biological Basis for Dose Limitation in the Skin, 20:(4), 1992.<br />

No. 60. 1990 Recommendations of the International Commission on Radiological Protection, 21:(1–3), 1991.<br />

No. 66. Human Respira<strong>to</strong>ry Tract Model for Radiological Protection, 24:(1–3), 1994.<br />

No. 68. Dose Coefficients for Intakes of Radionuclides by Workers, 24(4), 1994.<br />

No. 70. Basic Ana<strong>to</strong>mical and Physiological Data for use in Radiological Protection: The Skele<strong>to</strong>n, 25:(2), 1996.<br />

No. 79. Genetic Susceptibility <strong>to</strong> Cancer, 28:(1/2), 1998.

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