What are some examples of ionizing radiation?
There are natural and artificial sources of ionizing radiation. Artificial sources of radiation include X-ray machines, radioactive isotopes used in nuclear medicine, gamma cameras, nuclear gauges and nuclear power plants.
X-rays refer to a kind of electromagnetic radiation generated when a strong electron beam bombards metal inside a glass tube. The frequency of this radiation is very high— 0.3 to 30 EHz (exahertz or billion gigahertz). In comparison, FM radio stations transmit at frequencies around 100 MHz (megahertz) or 0.1 GHz (gigahertz).
Natural sources of radiation include:
Minerals such as uranium and thorium are radioactive and give off radiation when the nucleus breaks down or disintegrates. The three kinds of radiation generated by radioactive materials or sources are alpha particles, beta particles and gamma rays.
- context background radiation from space,
- context cosmic radiation from cosmic rays,
- context terrestrial radiation from minerals in the earth’s crust,
- context radiation from inhaling radon gas, and
- context radiation from ingesting food and drinking water that may contain radioactive potassium-40.
What properties are considered when ionizing radiation is measured?
Ionizing radiation is measured in terms of:
From the point of view of occupational exposure, the radiation dose is the most important measure. Occupational exposure limits such as the ACGIH TLVs® are given in terms of the permitted maximum dose. The risk of radiation-induced diseases depends on the total radiation dose a person receives over time.
- context the strength or radioactivity of the radiation source,
- context the energy of the radiation,
- context the level of radiation in the environment, and
- context the radiation dose or the amount of radiation energy absorbed by the human body.
What does half-life mean when people talk about radioactivity?
Radiation intensity from a radioactive source diminishes with time as more and more radioactive atoms (radionuclides) emit energy to become stable atoms. Radioactive decay is the decline in radiation intensity. Half-life is the time after which the radiation intensity is reduced by half. This happens because half of the radioactive atoms will have decayed in one half-life period. For example, a 50 Bq radioactive source will become a 25 Bq radioactive source after one half-life.
Half-lives differ widely from one radioactive material to another and range from a fraction of a second to millions of years.
What units are used for measuring radiation dose?
When ionizing radiation interacts with the human body, it gives its energy to the body tissues. The absorbed dose is the amount of energy absorbed per unit weight of the organ or tissue and is expressed in units of gray (Gy). One gray dose is equivalent to one joule of radiation energy absorbed per kilogram of organ or tissue weight. Rad is the old and still used unit of absorbed dose. One gray is equivalent to 100 rads.
1 Gy = 100 rads
Equal doses of all types of ionizing radiation are not equally harmful to human tissue. Alpha particles produce greater harm than beta particles, gamma rays and X-rays for a given absorbed dose, so 1 Gy of alpha radiation is more harmful than 1 Gy of beta radiation. To account for the way in which different types of radiation cause harm to tissue or an organ, the radiation dose is expressed as the equivalent dose in units of sievert (Sv). The dose in Sv is equal to the total external and internal "absorbed doses" multiplied by a "radiation weighting factor" (WR - see Table 2 below) and is important when measuring occupational exposures. Before 1990, this weighting factor was called Quality Factor (QF).
1 Excluding Auger electrons emitted from nuclei bound to DNA.
2 Radiation weighting factors for these neutrons may also be obtained by referring to the continuous curve shown in Figure 1, and equation 4.3, on page 66 of the English version of the 2007 Recommendations of the International Commission on Radiological Protection, ICRP Publication 103, published in 2007.
Source: The Canadian Radiation Protection Regulations, Schedule 2 (SOR/2000-203).
Equivalent dose is often referred to simply as "dose" in every day use of radiation terminology. The old unit of "dose equivalent" or "dose" was rem.
Dose in Sv = Absorbed Dose in Gy x radiation weighting factor (WR)
Dose in rem = Dose in rad x QF
1 Sv = 100 rem
1 rem = 10 mSv (millisievert = one thousandth of a sievert)
1 Gy air dose equivalent to 0.7 Sv tissue dose (UNSEAR 1988 Report p.57)
1 R (roentgen) exposure is approximately equivalent to 10 mSv tissue dose
- context Column 1 | Column 2
- context Item | Type of Radiation | Weighting Factor
- context 1 | Photons, all energies | 1
- context 2 | Electrons and muons, all energies1 | 1
- context 3 | Protons and charged pions | 2
- context 4 | Alpha particles, fission fragments and heavy ions | 20
- context 5 | Neutrons | A continuous function of neutron energy2
What is the relationship between SI units and non-SI units?
Table 3 shows SI units (International System of Units or Systéme Internationale d'unités), the corresponding non-SI units, their symbols, and the conversion factors.
- context Quantity | SI unit and symbol | Non-SI unit | Conversion factor
- context Radioactivity | becquerel, Bq | curie, Ci | 1 Ci = 3.7 x 1010 Bq= 37 Gigabecquerels (GBq)1 Bq = 27 picocurie (pCi)
- context Absorbed dose | gray, Gy | rad | 1 rad = 0.01 Gy
- context "Dose"(Equivalent dose) | sievert, Sv | rem | 1 rem = 0.01 Sv1 rem = 10 mSv
What is an "effective dose"?
The effective dose is the sum of weighted equivalent doses in all the organs and tissues of the body.
Effective dose = sum of [organ doses x tissue weighting factor]. Effective dose is measured in millisieverts (mSv) or sieverts (Sv).
Tissue weighting factors (Table 4) represent the relative sensitivity of organs for developing cancer.
1 The weighting factor for skin applies only when the skin of the whole body is exposed.
2 The weighting factor for the remainder organs and tissues applies to the arithmetic mean dose of the 13 remainder organs and tissues.
3 Hands, feet and the lens of an eye have no weighting factor.
Source: The Canadian Radiation Protection Regulations, Schedule 1 (SOR/2000-203).
- context Column 1 | Column 2
- context Item | Organ or Tissue | Weighting Factor
- context 1 | Gonads (testes or ovaries) | 0.08
- context 2 | Red bone marrow | 0.12
- context 3 | Colon | 0.12
- context 4 | Lung | 0.12
- context 5 | Stomach | 0.12
- context 6 | Bladder | 0.04
- context 7 | Breast | 0.12
- context 8 | Liver | 0.04
- context 9 | Esophagus | 0.04
- context 10 | Thyroid gland | 0.04
- context 11 | Skin1 | 0.01
- context 12 | Bone surfaces | 0.01
- context 13 | Brain | 0.01
- context 14 | Salivary glands | 0.01
- context 15 | All organs and tissues not listed in items 1 to 14 (remainder organs and tissues) collectively, namely the adrenals, extra-thoracic region, gallbladder, heart, lymphatic nodes, small intestine, kidney, muscles, pancreas, spleen, thymus and prostate or uterus/cervix2,3 | 0.05
- context 16 | Whole body | 1.0
What are the main ways to control radiation exposure?
The main ways to control radiation exposure include engineering controls, administrative controls and personal protective equipment. Examples of these controls include:
Approximately forty-four (44) percent of monitored workers worldwide are exposed to artificial sources of radiation. Of those workers exposed to artificial sources, seventy-five percent work in the medical sector. Table 5 shows trends in global radiological exposure of workers since the 1970s.
* Estimates of average effective dose per worker in a year.
** Uranium mining is included in the nuclear industry.
Source: Radiation: Effects and Sources, United Nations Environmental Programme (UNEP), 2016
- administrative Education and training
- requirement Reducing exposure time
- requirement Increasing the distance from the radiation source
- requirement Using a physical barrier that modifies the pathway between the worker and the source of radiation e.g., concrete or lead
- requirement Recording exposures
- requirement Providing health surveillance
- requirement Promoting a health and safety culture
- requirement Complying with established radiation exposure (dose) limits
- requirement Monitoring of exposures (individual and collective monitoring)
What are "working level" and "working level month"?
In underground uranium mines, as well as in some other mines, radiation exposure occurs mainly due to airborne radon gas and its solid short-lived decay products, called radon daughters or radon progeny. Radon daughters enter the body with the inhaled air. The alpha particle dose to the lungs depends on the concentration of radon gas and radon daughters in the air.
The concentration of radon gas is measured in units of picocuries per litre (pCi/L) or becquerels per cubic metre (Bq/m3) of ambient air. The concentration of radon daughters is measured in working level (WL) units which is a measure of the concentration of potential alpha particles per litre of air.
The worker's exposure to radon daughters is expressed in units of Working Level Months (WLM). One WLM is equivalent to 1 WL exposure for 170 hours.
1 WL = 130,000 MeV alpha energy per litre air
= 20.8 µJ (microjoules) alpha energy per cubic meter (m3) air
WLM = Working Level Month
= 1 WL exposure for 170 hours
1 WLM = 3.5 mJ-h/m3
Often people use the concentration of radon gas (pCi/L) in the air to estimate the WL level of radon daughters. Such estimates are subject to error because the ratio of radon to its decay products (radon daughters) is not constant.
Equilibrium factor is the ratio of the activity of all the short-lived radon daughters to the activity of the parent radon gas. Equilibrium factor is 1 when both are equal. Radon daughter activities are usually less than the radon activity, and hence, the equilibrium factor is usually less than 1.
Conversion of radon exposure units (equilibrium factor = 0.40)
1 WLM = 3.54 mJ-h/m3
1 MBq-h/m3 = 2.22 mJ-h/m3
1 MBq-h/m3 = 0.628 WLM
Annual exposure from measured radon concentration
(A) At home: assuming 7000 hours spend indoors per year
1 Bq/m3 = 0.0156 mJ-h/m3
1 Bq/m3 = 0.0044 WLM
1 WLM - 4 mSv
1 mJ-h/m3 = mSv
(B) At work: assuming 2000 hours per year
1 Bq/m3 = 0.00445 mJ-h/m3 = 0.00126WLM
1 mJ-h/m3 = 1.4 mSv
1 WLM = 5 mSv
Source: ICRP Publication 65, Protection against Radon at Home and Work
mJ-h/m3 = millijoule hours/per cubic metre
MBq-h/m3 = megabecquerel hours per cubic meter
Joule is unit of energy
1 J = 1 Watt-second = Energy delivered in one second by a 1 Watt power source
1 calorie = 4.2 J
MBq/m3 = megabecquerel per cubic metre
WLM = Working Level Months