Problem 76
Question
In the 1986 disaster at the Chernobyl reactor in the Soviet Union (now Ukraine), about \(\frac{1}{8}\) of the \(^{137} \mathrm{Cs}\) present in the reactor was released. The isotope \(^{137} \mathrm{Cs}\) has a half-life for \(\beta\) decay of 30.07 \(\mathrm{y}\) and decays with the emission of a total of 1.17 \(\mathrm{MeV}\) of energy per decay. Of this, 0.51 \(\mathrm{MeV}\) goes to the emitted electron and the remaining 0.66 \(\mathrm{MeV}\) to a \(\gamma\) ray. The radioactive \(^{137} \mathrm{Cs}\) is absorbed by plants, which are eaten by livestock and humans. How many \(^{137} \mathrm{Cs}\) atoms would need to be present in each kilogram of body tissue if an equivalent dose for one week is 3.5 \(\mathrm{Sv}\) ? Assume that all of the energy from the decay is deposited in that 1.0 \(\mathrm{kg}\) of tissue and that the RBE of the electrons is 1.5.
Step-by-Step Solution
VerifiedKey Concepts
Chernobyl disaster
Cesium-137 is a radioactive isotope that was a major component of the fallout from the disaster. It played a significant role in the long-term environmental impacts, as it was spread over a large area. Being soluble in water, it easily entered the ecosystem, contaminating plants and animals, which, in turn, posed risks to humans through the food chain.
The Chernobyl disaster highlighted the dangers of nuclear power when safety systems are neglected or fail. It led to massive efforts to clean up and contained extensive international research into radiation safety and nuclear energy protocols.
Radioactive decay
Beta decay involves the transformation of a neutron into a proton, with the emission of an electron (beta particle) and an antineutrino. The emitted electron carries away a portion of the decay energy, and in this scenario, it accounts for 0.51 MeV.
Understanding radioactive decay is crucial for evaluating how long an isotope remains hazardous. For Cesium-137, with a half-life of approximately 30.07 years, we can calculate how much time will pass until its radioactivity diminishes by half. This long half-life means it remains hazardous for extended periods, requiring careful management and disposal.
137-Cs isotope
Cesium-137 decays with the release of 1.17 MeV of energy per decay. This energy is divided between 0.51 MeV to the emitted electron and 0.66 MeV to a gamma ray. These emissions pose health risks, since gamma rays can penetrate body tissues and cause damage at the cellular level.
Due to its chemical characteristics, Cesium-137 can easily become part of biological systems. Once it enters the food chain, it can accumulate in the body tissue of living organisms, posing internal radiation risks. This makes handling and monitoring of this isotope essential in the context of nuclear safety.
Energy deposition
In the exercise, energy deposition is crucial for calculating the radiation dosage. The equivalent dose, measured in sieverts, accounts for energy deposited per kilogram of tissue. This is determined by the absorbed dose and further adjusted by the Relative Biological Effectiveness (RBE).
Energy deposition calculations help us understand how much radiation different tissues in the body receive. For Cesium-137, all decay energy is assumed to be deposited into 1 kg of tissue. This simplification is critical for calculating potential biological effects and understanding safety limits.
Biological effectiveness
This concept is quantified as the Relative Biological Effectiveness (RBE). RBE is used to compare the biological impact of radiation types: It's the factor by which an absorbed dose is multiplied to reflect its actual biological damage. For electrons, the RBE is often taken as 1.5, meaning electrons are 1.5 times more damaging biologically than other forms of radiation under specific conditions.
Understanding RBE is vital when calculating radiation doses and assessing the potential health risks from exposure. It allows us to adjust for the type and energy of radiation involved, providing a more accurate estimation of risk to living organisms.