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

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RADIATION SAFETY GUIDES 421<br />

Substituting this value in<strong>to</strong> Eq. (8.68) and solving for the dose rate gives<br />

˙D =<br />

f DAC<br />

0.114<br />

0.33<br />

= = 2.9 mrems/h.<br />

0.114<br />

Since the dose rate in this example exceeds 2.9 mrems/h, wearing a respira<strong>to</strong>r would<br />

decrease the worker’s efficiency, thereby increasing his or her <strong>to</strong>tal exposure time<br />

and leading <strong>to</strong> a greater TEDE than if he or she had not worn a respira<strong>to</strong>r. In this<br />

case, the worker would have received a TEDE of 12.7 mrems with a respira<strong>to</strong>r but<br />

only 11.7 mrems without a respira<strong>to</strong>r.<br />

ECOLOGICAL RADIATION SAFETY<br />

SUMMARY<br />

Radioecology and environmental health physics evolved mainly in the context of<br />

risk assessment <strong>to</strong> humans, and thus may be considered anthropocentric. To this<br />

end, radiation-exposure pathways and potential exposure <strong>to</strong> humans from naturally<br />

occurring radioiso<strong>to</strong>pes and from residual anthropogenic environmental radioactivity<br />

was extensively studied. A long-term (25 years) study of the environmental and<br />

human-health effects from a nuclear power plant that discharged liquid radioactive<br />

waste in<strong>to</strong> a major river within the guidelines of the U.S. NRC found that the releases<br />

had no known environmental or human-health impact. It was believed that<br />

the environmental radiation safety standards that had been developed would also<br />

be protective of the biosphere. This belief seems reasonable, since all life evolved in<br />

a higher radiation environment than the present one. Now there is an increasing<br />

societal concern about the health of the environment. However, there is no universally<br />

accepted agreement about what we mean by the “environment.” In the case of<br />

nonhuman species, for example, are we interested in protecting individual members<br />

of the species, as in the case of humans, or is our interest in protecting the<br />

species in the interests of biodiversity? To answer some of these questions, the ICRP<br />

has suggested that a framework be developed for assessing the impact of ionizing<br />

radiation on nonhuman species.<br />

The harmful effects of overexposure <strong>to</strong> ionizing radiation were seen almost immediately<br />

after the discovery of X-rays and its introduction in<strong>to</strong> medicine, science,<br />

and industry. Initially, the incidence rate of cancer and other harmful effects among<br />

users of radiation was relatively high. For example, during the period 1929–1949, the<br />

death rate of radiologists from leukemia was nine times greater than the leukemia<br />

death rate among nonradiologist physicians. Today, the leukemia rate among radiologists<br />

is no greater than among their nonradiologist colleagues. Furthermore, the<br />

nuclear industry <strong>to</strong>day is among the safest of all industrial enterprises. Eight different<br />

epidemiological studies of 15,674 deaths among 77,000 nuclear workers found<br />

the overall standardized mortality ratio (SMR) for all causes of death <strong>to</strong> be 82 and<br />

the SMR for cancer deaths <strong>to</strong> be 90. (An SMR of 100 means that the actual number

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