Units of measure and exposure
The measure of gamma rays' ionizing ability is called the exposure:
- The coulomb per kilogram (C/kg) is the SI unit of ionizing radiation exposure, and is the amount of radiation required to create 1 coulomb of charge of each polarity in 1 kilogram of matter.
- The röntgen (R) is an obsolete traditional unit of exposure, which represented the amount of radiation required to create 1 esu of charge of each polarity in 1 cubic centimeter of dry air. 1 röntgen = 2.58×10−4 C/kg
However, the effect of gamma and other ionizing radiation on living tissue is more closely related to the amount of energy deposited rather than the charge. This is called the absorbed dose:
- The gray (Gy), which has units of (J/kg), is the SI unit of absorbed dose, and is the amount of radiation required to deposit 1 joule of energy in 1 kilogram of any kind of matter.
- The rad is the deprecated CGS unit, equal to 0.01 J deposited per kg. 100 rad = 1 Gy.
The equivalent dose is the measure of the biological effect of radiation on human tissue. For gamma rays it is equal to the absorbed dose.
- The sievert (Sv) is the SI unit of equivalent dose, which for gamma rays is numerically equal to the gray (Gy).
- The rem is the deprecated CGS unit of equivalent dose. For gamma rays it is equal to the rad or 0.01 J of energy deposited per kg. 1 Sv = 100 rem.
Properties
Shielding
Shielding from gamma rays requires large amounts of mass, in contrast to alpha particles which can be blocked by paper or skin, and beta particles which can be shielded by foil. Gamma rays are better absorbed by materials with high atomic numbers
and high density, although neither effect is important compared to the
total mass per area in the path of the gamma ray. For this reason, a
lead shield is only modestly better (20–30% better) as a gamma shield,
than an equal mass of another shielding material such as aluminium,
concrete, water or soil; lead's major advantage is not in lower weight,
but rather its compactness due to its higher density. Protective
clothing, goggles and respirators can protect from internal contact with
or ingestion of alpha or beta emitting particles, but provide no
protection from gamma radiation from external sources.
The higher the energy of the gamma rays, the thicker the shielding
made from the same shielding material is required. Materials for
shielding gamma rays are typically measured by the thickness required to
reduce the intensity of the gamma rays by one half (the half value layer or HVL). For example gamma rays that require 1 cm (0.4″) of lead to reduce their intensity by 50% will also have their intensity reduced in half by 4.1 cm of granite rock, 6 cm (2½″) of concrete, or 9 cm (3½″) of packed soil. However, the mass of this much concrete or soil is only 20–30% greater than that of lead with the same absorption capability. Depleted uranium is used for shielding in portable gamma ray sources, but here the savings in weight over lead are larger, as portable sources' shape
resembles a sphere to some extent, and the volume of a sphere is
dependent on the cube of the radius; so a source with its radius cut in
half will have its volume reduced eight times, which will more than
compensate uranium's greater density (as well as reducing bulk). In a
nuclear power plant, shielding can be provided by steel and concrete in
the pressure and particle containment vessel, while water provides a
radiation shielding of fuel rods during storage or transport into the
reactor core. The loss of water or removal of a "hot" fuel assembly into
the air would result in much higher radiation levels than when kept
under water.
Matter interaction
The total absorption coefficient of aluminium (atomic number 13) for
gamma rays, plotted versus gamma energy, and the contributions by the
three effects. As is usual, the photoelectric effect is largest at low
energies, Compton scattering dominates at intermediate energies, and
pair production dominates at high energies.
When a gamma ray passes through matter, the probability for
absorption is proportional to the thickness of the layer, the density of
the material, and the absorption cross section of the material. The
total absorption shows an exponential decrease of intensity with distance from the incident surface:
where x is the distance from the incident surface, μ = nσ is the absorption coefficient, measured in cm−1, n the number of atoms per cm3 of the material (atomic density) and σ the absorption cross section in cm2.
As it passes through matter, gamma radiation ionizes via three processes: the photoelectric effect, Compton scattering, and pair production.
- Photoelectric effect: This describes the case in which a gamma photon interacts with and transfers its energy to an atomic electron, causing the ejection of that electron from the atom. The kinetic energy of the resulting photoelectron is equal to the energy of the incident gamma photon minus the energy that originally bound the electron to the atom (binding energy). The photoelectric effect is the dominant energy transfer mechanism for X-ray and gamma ray photons with energies below 50 keV (thousand electron volts), but it is much less important at higher energies.
- Compton scattering: This is an interaction in which an incident gamma photon loses enough energy to an atomic electron to cause its ejection, with the remainder of the original photon's energy emitted as a new, lower energy gamma photon whose emission direction is different from that of the incident gamma photon, hence the term "scattering". The probability of Compton scattering decreases with increasing photon energy. Compton scattering is thought to be the principal absorption mechanism for gamma rays in the intermediate energy range 100 keV to 10 MeV. Compton scattering is relatively independent of the atomic number of the absorbing material, which is why very dense materials like lead are only modestly better shields, on a per weight basis, than are less dense materials.
- Pair production: This becomes possible with gamma energies exceeding 1.02 MeV, and becomes important as an absorption mechanism at energies over 5 MeV (see illustration at right, for lead). By interaction with the electric field of a nucleus, the energy of the incident photon is converted into the mass of an electron-positron pair. Any gamma energy in excess of the equivalent rest mass of the two particles (totaling at least 1.02 MeV) appears as the kinetic energy of the pair and in the recoil of the emitting nucleus. At the end of the positron's range, it combines with a free electron, and the two annihilate, and the entire mass of these two is then converted into two gamma photons of at least 0.51 MeV energy each (or higher according to the kinetic energy of the annihilated particles).
The secondary electrons (and/or positrons) produced in any of these
three processes frequently have enough energy to produce much ionization themselves.
Additionally, gamma rays, particularly high energy ones, can interact with atomic nuclei resulting in ejection of particles in photodisintegration, or in some cases, even nuclear fission (photofission).
The total absorption coefficient of lead (atomic number 82) for gamma
rays, plotted versus gamma energy, and the contributions by the three
effects. Here, the photoelectric effect dominates at low energy. Above 5
MeV, pair production starts to dominate.
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