Minimizing Radiation Exposure

Chapter 23 Minimizing Radiation Exposure



Many perioperative nurses are involved with diagnostic, interventional, and therapeutic procedures in medical facilities that use ionizing radiation. Medical facilities that use ionizing radiation must have an established radiation safety program (RSP) with policies and procedures designed to protect the patient, health care workers, nurses, and physicians. The goal of the program is to ensure safety in these environments and minimize exposure to ionizing radiation. In order to use radioactive materials the facility must have a radioactive material license or permit with a state or the U.S. Nuclear Regulatory Commission (NRC). Facilities using radiation-producing machines for diagnostic x-ray examination and fluoroscopy must register each machine with the state. In each situation a radiation safety officer is designated as the individual responsible for managing the RSP. A successful RSP protects patients, radiation health care workers, members of the public, and the environment from ionizing radiation used in the facility.


Perioperative nurses are a critical component to successfully implementing the RSP because they are the “end user,” the person who works directly with the patients undergoing procedures involving ionizing radiation. It is the goal of this chapter to provide perioperative nurses with practical information pertaining to the safe use of ionizing radiation, facilitating care and answering patients’ questions regarding care specifics, and enhancing awareness of best practices when working around ionizing radiation.



TYPES OF IONIZING RADIATION


The term radiation is very broad; this discussion will focus on radiation that has the ability to cause ionization. Ionization is the process of removing or converting electrons from atoms. Ionizing radiation can be created from radiation-producing machines such as diagnostic x-ray units. Another source of ionizing radiation comes from radionuclides. A radionuclide is an atom with an unstable nucleus. The unstable nucleus is characterized as having excess energy, which is available to be imparted either to a newly created radiation particle within the nucleus or to an atomic electron. The radionuclide in this process undergoes radioactive decay and emits gamma ray(s) and/or particles. These rays and particles constitute ionizing radiation. Radionuclides may occur naturally but can also be artificially produced.


There are many types of ionizing radiation such as beta particles, gamma radiation, x-rays, positrons, alpha particles, and neutrons. The primary types of radiation used in the diagnosis and treatment of disease are gamma radiation, x-rays, and positrons. Occasionally beta radiation is used. Each of these types of radiation will be reviewed.







RADIATION EXPOSURE


Radiation exposure is defined as the transfer of energy in air from gamma or x-ray radiation. Radiation exposure is measured in roentgen (R), and exposure rate is quantified as roentgen/hour (R/hr) or, in smaller terms, as milliroentgen/hour (mR/hr). In the International System of Units (SI), the measure of radiation exposure is expressed in units of coulomb/kilogram. Another radiation dose unit is the roentgen absorbed dose (rad). This is the measure of the absorption of energy per unit mass by an object as a result of radiation interactions. In SI units the unit for radiation dose is the gray (Gy), where 1 Gy = 100 rad. Because different types of radiation cause varying degrees of damage to biological tissue, a system of estimating the potential harm was developed. The term rem is used to report the “equivalent dose” from exposure to different types of radiation. The rem is related to the rad by use of a radiation quality factor to account for the differences in damage done to tissues. In the SI system the unit of equivalent dose is sievert (Sv), where 1 Sv = 100 rem. The equivalent dose is the term used by the regulators to describe the radiation exposure that individuals may receive while working with or around ionizing radiation. These terms are often used interchangeably, which is incorrect. Simply stated, the roentgen refers to ionization of air, the rad refers to ionizing radiation energy deposited in matter, and the rem refers to the ability or tendency of ionizing radiation to cause harm to tissues.



BIOLOGICAL EFFECTS OF IONIZING RADIATION


The use of x-ray, gamma, and positron ionizing radiation for patient diagnosis and treatment can be quite disconcerting to the patient, as well as the perioperative nurse responsible for the care of the patient. It is not uncommon for staff and patients to raise questions regarding the safety of procedures involving ionizing radiation. Radiation health effects have been studied extensively. Evidence of human radiation health effects comes from many sources, but primarily from the studies of the survivors of the atomic bombings in Japan, uranium miners, radium dial painters, and medical studies. The Japanese Life Span Study was designed to evaluate the late mortality effects of the radiation and other trauma received by the survivors of the Hiroshima and Nagasaki A-19 atomic bombs. The sample population consisted of approximately 100,000 persons, including those exposed near to ground zero, persons exposed at such distances from ground zero as to guarantee that little radiation was received, and nonexposed immigrants to the cities (Beebe et al, 1961). The information obtained from these studies indicates a linear increase in adverse health effects from relatively large doses of radiation. There is minimal evidence to support increased risk to people at lower levels of radiation.


High levels of radiation are known to have an adverse effect on cells. Cells that are rapidly dividing, such as reproductive cells, blood-forming tissues, skin, and the gastrointestinal tract, are more sensitive to ionizing radiation. If a cell is exposed to ionizing radiation, several outcomes are possible. The cell can have no observed damage and continue to thrive; the cell may be damaged and die following division; it can become damaged but repair itself; or it can become damaged and misrepair itself, resulting in a change in cellular function, with the damage passing onto the next generation of cells. In the last scenario the formation of cancer results from changes in the cell’s reproductive structure such that the cells can replicate into precancerous cells, which may eventually become cancerous. If the cells can be affected by ionizing radiation, then one must consider the result of ionizing radiation on living organisms. To better understand the effect that ionizing radiation has on living organisms, two types of health effects must be defined: deterministic health effects and stochastic health effects.




Stochastic Health Effects


Stochastic health effects are health effects that occur by chance. Stochastic health effects are based on the probability of a health effect occurring and not on the severity of the effect. Regardless of a person’s exposure to ionizing radiation, there is the random chance that the individual may or may not develop cancer in his or her lifetime. The conservative assumption is, if one is exposed to radiation, there is a future, random chance of developing an adverse health effect such as cancer. Therefore the probability of a health effect occurring is proportional to the radiation dose. However, there are no early observable effects from exposure to low levels of ionizing radiation, but adverse health effects such as cancer may occur many years later. The challenge is that radiation-induced cancer is not distinguishable from cancer caused by other factors. The other factors that can contribute to a cancer are inherited traits, age, sex, physical condition, diet, cigarette smoking, and exposure to other agents.


To further understand the difference between deterministic and stochastic health effects, the terms acute dose and chronic dose will be used, respectively. With an acute dose the individual receives a radiation dose in a very short time period. If the radiation dose is large enough, adverse health effects such as reddening of the skin, loss of hair, damage to the gastrointestinal tract, and damage to the central nervous system may occur within hours or a few days after exposure. If the acute radiation levels are high enough, death may occur.


On the other hand, with chronic dose, the individual may be exposed to low levels (a few millirem [mrem] each week) of ionizing radiation over their working lifetime. These chronic doses are unlikely to cause deterministic health effects, as a result of repair of damaged cells, but may cause a delayed health effect. Exposure to large amounts of sunshine is a good analogy for explaining acute and chronic doses. If an individual were to receive an acute exposure to the sun, a severe sunburn such as skin blistering and peeling may develop. If another individual were to receive chronic, low doses of sun, it may result in a golden tan year after year. Now assume that both the sunburned individual and the tanned individual reach the age of 75 and both are diagnosed with skin cancer. The sunburned individual may develop skin cancer as a result of the one-time acute sunburn, or the sun-tanned individual may develop skin cancer as a result of the chronic, low levels of exposure to the sun over many years. Both scenarios may lead to skin cancer, and yet there are so many other factors that have not been accounted for, such as inherited traits, age, and sex, that it is almost impossible to differentiate between the skin cancers that were a result of either acute or chronic exposure to the sun.


In a medical facility the possibility of a radiation health care worker receiving a high acute dose of ionizing radiation is extremely unlikely because of the presence of a RSP involving dose monitoring, education, and dose-reduction strategies. The main concern is for those health care workers who receive chronic, low levels of radiation exposure over their working lifetime. There are many dose-response models that describe the relationship between radiation dose and health effects. For doses greater than 50 rem (500 mSv), there is a definite linear relationship between dose and additional cancer risk (NRC, 1996). Fifty rem (500 mSv) is 10 times higher than the current annual limit of 5 rem (50 mSv). Below 50 rem (500 mSv), there is no definitive relationship between dose and additional cancer risk. Because of the uncertainty in the dose-response relationship at doses below 50 rem (500 mSv), it is assumed that there is a linear zero threshold-dose response at the lower levels of radiation dose. This means that all radiation doses are assumed to have some adverse effect. This is a conservative assumption that serves as the basis for our radiation protection programs throughout the world. By incorporating the philosophy of maintaining exposures from levels of ionizing radiation as low as reasonably achievable, additional effort is made to minimize radiation doses to health care workers and members of the public.


Another category of stochastic health effects that warrants attention is the perception that radiation and birth defects are directly linked. This is often referred to as hereditary effects. If a woman is exposed to ionizing radiation and later has children, there is the misperception that the offspring will exhibit birth defects or an increased risk for cancer. This has not been observed in studies of exposed humans, and the possibility of hereditary effects exists only from studies performed on animals. For this reason, additional precautions are recommended to continuously minimize exposure to ionizing radiation. To protect against deterministic and stochastic health effects, RSPs at medical facilities incorporate procedures and policies to protect radiation workers, patients, and the public from external and internal exposure to ionizing radiation.


Finally, teratogenic effects are developmental effects caused by intrauterine exposure to ionizing radiation. Irradiation of the developing fetus is a concern because of the rapidly dividing and developing cells. The risk to the fetus is a function of gestational age at the time of radiation exposure and the radiation dose. Based on this information, the risk from ionizing radiation to the fetus and children is higher than that for adults. The data to support a teratogenic effect come from experiments using animal models and from human populations exposed to very high doses of radiation such as the atomic bomb survivors. For humans the significant teratogenic effects observed included mental retardation, intrauterine growth retardation, and cancer development such as childhood leukemia. However, not all exposures to ionizing radiation cause these effects. For most diagnostic procedures involving ionizing radiation in which the fetal dose is less than 10 rem (100 mSv), very little data exist to support teratogenic effects in humans (Duke University, 2009; Edwards, n.d.). Even though there is very little evidence of teratogenic health effects below 10 rem (100 mSv), there is enough cause for concern that RSPs have established additional policies for the declared pregnant health care worker and the pregnant patient intended to further reduce the radiation dose to the fetus. The focus of this chapter is on the health care worker, and radiation safety policies for the declared pregnant health care worker will be discussed in greater detail later in this chapter.



RADIATION DOSE LIMITS


Based on the discussion regarding biological effects from exposure to ionizing radiation, it is prudent to explain radiation dose limits and how they are applied to protect individuals. Regulatory agencies have established specific limits of radiation dose for those working with ionizing radiation and for those considered members of the general public. Those individuals working with or around ionizing radiation that have been trained are considered occupational radiation workers. Individuals who work in or near areas where ionizing radiation is used, but are not directly involved in its use, are frequently referred to as ancillary personnel. Administrative staff, housekeeping, and maintenance staff may be considered ancillary personnel. These individuals may receive minimal training on radiation safety awareness. The term general public is applied to those individuals who are not directly working with ionizing radiation and who do not receive radiation safety training. Occupational radiation workers are limited to 5 rem (50 mSv) per year. Ancillary personnel and the general public are limited to 0.1 rem (1 mSv) in a year and less than 0.002 rem (0.02 mSv) in any hour. Annual dose limits in the United States are listed in Table 23-1 (NRC, 2009).


TABLE 23-1 Annual Dose Limits in the United States


















Total whole body dose (occupational) 5 rem/year (50 mSv/year)
Lens of the eye (occupational) 15 rem/year (150 mSv/year)
Skin (occupational) 50 rem/year (500 mSv/year)
Extremities (occupational) 50 rem/year (500 mSv/year)
Members of the general public and ancillary personnel 0.1 rem/year (1.0 mSv/year) not to exceed 0.002 rem (0.02 mSv) in any hour

From U.S. Nuclear Regulatory Commission: Occupational dose limits for adults, 10 CFR 20.1201, April 2009; U.S. Nuclear Regulatory Commission: Dose limits for individual members of the public, 10 CFR 20.1301, April 2009.




Declared Pregnancy Policy


A declared pregnancy policy applies to pregnant women whose assigned duties involve exposure to ionizing radiation. Exposure to any amount of radiation is assumed to carry some amount of risk. The conservative assumption is that as the dose increases, the likelihood of biological effects from the radiation increases as well. The annual limit of radiation exposure for an occupationally exposed worker is 5 rem (50 mSv). Although this limit is designed to protect the adult radiation worker, there is also another recommended limit for the embryo/fetus of declared pregnant radiation workers. The embryo/fetus of a declared pregnant worker is limited to 0.5 rem (5 mSv) over the gestation period. A declared pregnancy policy is designed to protect the fetus of an occupationally exposed health care worker. The staff working with and around ionizing radiation have the option to declare their pregnancy in writing to their employer. This is a voluntary decision. A woman may choose to make a formal declaration at any point in her pregnancy, or she may choose not to make a formal declaration at all. In the latter case the dose to the embryo/fetus would not be evaluated or limited by the facility. However, the woman’s dose would still be subject to the limit for occupational radiation workers, typically 5 rem (50 mSv) per year.


Work restrictions for the declared pregnant health care worker are required if there is a significant potential for the embryo/fetus to receive a dose in excess of the 0.5 rem (5 mSv) limit as a result of the external exposure of its mother and/or from intakes of radioactive material by its mother. The expectation is that the radiation dose would be received at an even rate over the entire gestation period. To accurately assess the fetal dose, it is recommended that the declared pregnant health care worker receive a fetal dosimeter, which should be worn at the abdomen at about waist level (Figure 23-1). If the worker wears an x-ray–shielding apron, the fetal dosimeter must be worn under the apron. The fetal dosimeter should be exchanged monthly for analysis. A facility may elect to purchase maternity lead aprons designed specifically for use by the pregnant health care worker. Most maternity lead aprons increase lead shielding from 0.5 mm to 1.0 mm in areas to protect the fetus.


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Aug 5, 2016 | Posted by in ANESTHESIA | Comments Off on Minimizing Radiation Exposure

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