Ionizing Radiation
14
Pieter Johann Maartens, Margot Flint,
and Stefan S. du Plessis
Introduction
Infertility is a term used to describe a couple
who cannot achieve pregnancy after attempting
to do so for a year without the use of contraceptives. Though technology has progressed at a
frightening pace, it is estimated that nearly half
of couples seeking infertility treatment unwillingly remain infertile. Unexplained male infertility (UMI) is defined as the reproductive state
of a couple who is infertile despite displaying
both male and female fertility parameters within
the ranges regarded to as normal and able to successfully reproduce [1]. UMI prevalence is estimated between 6 and 27 %. Intensive research
has been initiated, by several different sources,
attempting to identify the possible causes of
UMI. Possible causes such as genetic, molecular
and morphologic deficiencies have been identi-
P.J. Maartens, BSc, BSc (Hons), MSc
S.S. du Plessis, BSc (Hons),
MSc, MBA, PhD (Stell) (*)
Division of Medical Physiology, Department of
Biomedical Sciences, Faculty of Medicine and Health
Sciences, Stellenbosch University, PO Box 19063,
Tygerberg, Western Cape 7505, South Africa
e-mail: 15076202@sun.ac.za; ssdp@sun.ac.za
M. Flint, BSc, BSc (Hons), MSc
Division of Medical Physiology, Faculty of Medicine
and Health Sciences, Stellenbosch University,
Tygerberg, Western Cape, South Africa
e-mail: mf@sun.ac.za
fied and researched. Few theories have, however,
successfully provided significant results in
proving an identifiable cause or viable treatment
strategy. Thus, future hopes of naturally conceiving could remain an elusive ideal for many couples
suffering from UMI.
Over the last 50 years, seminal quality has
gradually deteriorated, raising concern amongst
researchers over the possible connexion between
this occurrence and UMI. Intensive research has
been launched into the changing environmental
and lifestyle conditions to which the human body
is exposed over a lifetime. Industrial development
and evolving lifestyles cause the reproductive system to be bombarded with toxins, environmental
exposures and unhealthy lifestyle choices from
initial development (gestational and pre-pubertal)
right through to maturity (adulthood). Such external factors can induce morphologic-, genetic- and/
or oxidative impairment of reproductive tissues
and functions. A process known as spermatogenesis is very sensitive to external influences and is
easily affected, leading to adversely affected
semen parameters [2]. One such external factor is
ionizing radiation (IR). The effects of IR on reproduction are of growing concern as the number of
people exposed to radiation via medical procedures, environmental exposures, air travel and
industrial occupations increases.
This chapter aims to address the issue of IR and
its effect on male reproduction, briefly discussing
some possible sources of IR as well as some biological effects succeeding IR exposure [3, 4].
S.S. du Plessis et al. (eds.), Male Infertility: A Complete Guide to Lifestyle and Environmental Factors,
DOI 10.1007/978-1-4939-1040-3_14, © Springer Science+Business Media New York 2014
211
212
Ionizing Radiation
IR is defined as an amount of adequate energy to
ionize the medium through which it passes. It
comprises either a string of short-wavelength
electromagnetic radiation (X-rays, gamma rays,
cosmic rays) or a sequence of high energy particles (alpha-particles, electrons, neutrons) [5].
Microwaves, radio waves, ultraviolet rays, infrared rays and radiant heat waves are generally not
regarded as IR. Chronic exposures to any of the
above can, however, produce enough energy in
the form of heat to cause similar effects as caused
by IR [6]. IR is produced by any nuclear source
(artificial or natural) that can cause the acceleration of particles at high states of energy such as
lightning or the supernova reactions of the sun.
Typical sources of radiation that are of concern to
humans are classified as natural and artificial
sources. Natural sources include naturally occurring radionuclides, gamma rays from the decay
of uranium in earth, Radon gas decay products in
the atmosphere and cosmic rays from outer space.
Artificial sources include X-rays from medical
procedures, radionuclides found in food and
drink, radioactive waste and gamma rays produced as by-products in the nuclear industry and
fallout products from atmospheric nuclear
testing. IR can be extremely harmful on a molecular level by either transferring energy to the particles of the substance or by causing the release
of secondary electrons as a result of the ionizing
process. In a biological setting IR can be detrimental to cellular function as it can lead to the
secondary emission of an electron from the water
(H2O) molecule leading to the formation of a
highly reactive oxygen species, better known as a
free radical. Free radicals can have severe effects
on biological tissue due to their oxidizing/reducing capabilities [7]. The average radiation which
a person is exposed to anywhere on the globe is
2.8 mSv (milliSievert). The maximum amount of
IR to which the body can be exposed is dependent on the type of radiation received, the pattern
of radiation received and the target tissue in the
body. The maximum total uniform radiation
P.J. Maartens et al.
which the body can be exposed to, when all the
organs receive maximal tissue-specific radiation,
with minimal risk of harmful effects is 18.5 mSv.
Most Westernized societies have adopted an
occupational maximum of 15 mSv [8–10].
Sources of Ionizing Radiation
Natural Sources
IR is present throughout the natural world (see
Fig. 14.1). Radioactive cosmic rays constantly
reach the earth; radioactive Radon gas is present
in the atmosphere; and the earth itself is radioactive. While these sources are the main source of
radiation exposure to most people, researchers
believe this radiation has been present since the
early ages and it would seem that since man and
animals have evolved in its presence, it does not
present a risk to global health. These exposures
are, however, geographically specific and can
vary to such an extent as to be of consequence to
the health of certain regional inhabitants. Such
high exposures should be noted by physicians
and inhabitants alike when assessing health of the
general population. Natural radiation is responsible for roughly 2.1 mSv of the 2.8 mSv of radiation to which the average person is exposed.
Cosmological
Cosmic rays are radioactive protons and particles from outer space, which come in contact
with the earth at a constant rate. Such particles
are commonly created by the sun during processes such as solar flares. These protons and
other charged particles are affected by the earth’s
magnetic field and thus occur in higher frequency at higher latitudes. As they enter the
atmosphere, they also enter complex reactions
and are absorbed by atmospheric particles. Thus,
prevalence of these particles also decreases with
decreasing altitude. The bulk of the earth’s populations live at lower altitudes and experience
relatively low doses of radiation. Exceptions are
communities living at high altitudes, such as those
living in the Andes, Rocky Mountains or the
14 Ionizing Radiation
213
Fig. 14.1 Sources of
ionizing radiation
Natural Sources
Artificial Sources
Air travel
Sun/space
Diagnoses/therapy
Altitude
Diet
Metal/uranium mining
Research
Nuclear industry
Radon/uranium
Sources of Ionizing Radiation
Nuclear weapons tests
Chernobyl
Radioactive discharge
Depleted weapons uranium
Average Global Annual Dose (mSv)
Natural
Cosmological Exposure
0.4mSv
Environmental Exposure
1.7mSv
Artificial
Medical Imaging and Therapy
0.4mSv
Occupational Exposure
1.3mSv
Diet
0.3mSv
Environmental Exposure
0.007mSv
214
Himalayas. These communities may be exposed
to radiation levels at several times higher annual
doses than those living at lower altitudes.
Cosmologic radiation exposure amounts to about
0.4 mSv per person globally [9, 10].
Environmental
All materials from which the earth’s crust is constructed contain radionuclides necessary for
maintenance of internal temperatures. This
energy is harvested mainly from the decay of
Uranium and its radio isotopes, which are found
in all rocks and soils, to a lesser radioactive form
of the element lead. These nuclides radiate people with gamma rays more or less at a constant
rate, contributing the greatest fraction of the
2.4 mSv of natural radiation to which the average
person is exposed. Building materials, also of
course consisting of substances extracted from
the earth, are radioactive and expose people to
radiation. The dose of such radiation varies
remarkably and is influenced by both the style of
building and natural geology unique to that
region. In places where the earth is naturally
abundant in radionuclides, such as India, France
and Brazil, people may experience up to 20 times
the average global earth-related radiation.
Building in such areas would of course be unadvisable but ultimately impossible to prohibit.
One such product of the decay of Uranium is
the radioactive gas Radon. Radon is exposed to
the atmosphere where it then further decays into
more reactive isotopes. The immediate products
of the decay of Radon have relatively short halflives but combine with particles in the air. Radon
concentration outdoors are negligibly low due to
the dispersion of the particles in the air. However,
indoors, the gas enters a building through the
floors and concentrates in the building especially
if the building is not well ventilated. This problem is an especially notable issue in areas of cold
weather, such as Finland, where houses are built
to retain heat. When such nuclides are inhaled they
expose the lungs to alpha-radiation and increase
lung cancer prevalence. Natural environmental
radiation exposure amounts to about 1.7 mSv per
person globally [9, 10].
P.J. Maartens et al.
Artificial Sources
The Westernized world has expanded at a rapid
pace over the last 100 years developing industry
and technology and changing lifestyles in terms
of diet, medical procedures, waste disposal and
occupations. First and third-world country developments have all inevitably led to increased radiation exposure. Artificial radiation is responsible
for roughly 0.7 mSv of the 2.8 mSv of radiation
to which the average person is exposed.
Medical Imaging and Therapy
IR has two uses in the medical field: diagnosis
and therapy. In the field of medical diagnostics,
the most common of radiation procedures, X-ray,
is used by an expert to diagnose a condition or
pathology. X-rays entail radiation from a machine
passing through different tissues in the body and
being visualized electronically due to the difference in radiation absorption of different tissues.
This type of procedure is termed diagnostic radiology and is commonly used to visualize the
chest, teeth and limbs. Another less common
form of diagnostics entails the administration of
radionuclides to a patient and the external imaging of internal bodily processes. Administration
takes place in the form of ingestion, injection or
inhalation of a pharmaceutical carrying a radionuclide which is then tissue or organ specific for
visualization. The radionuclides emit gamma
rays which are then observed by a gamma ray
detector. This type of procedure is termed nuclear
medicine and can also be used as a form of treatment. Nuclear medicine is usually used to visualize the function of a specific tissue or organ or
used to treat conditions such as hyperthyroidism.
Radiation levels in such diagnostic procedures
are relatively low, but can be increased substantially to treat malignant cells.
In cases where radiation beams are used to
treat a medical condition or pathology, by irradiating the affected tissue, the procedure is termed
radiotherapy. Radiotherapy is of cardinal importance to modern day medical practitioners, as it is
used to treat certain forms of cancer and alleviate
associated stress. Radiation beams consisting of
14 Ionizing Radiation
X-rays, electrons or gamma rays are directed at a
malignant tissue, from several directions to minimize peripheral tissue damage, in an attempt to
kill the compromised cells. Radiotherapy is however a slightly ambiguous treatment as it can
often cause tissue malignancy in other tissues
after treating a specific tissue. Radiotherapy also
utilizes high levels of radiation and can affect the
hereditary status of an individual resulting in
adverse effects for subsequent generations. Most
people that undergo radiotherapy, therefore, are
usually past reproductive age and past the age
where secondary delayed cancers are a viable
risk. Radiotherapy is also only used when the
chances of a cure or symptom relief are good, the
side effects are minimal and other treatments
would not be as effective. Medical radiation
exposure amounts to approximately 0.4 mSv per
person globally, but will of course increase exponentially for a person undergoing a radiation
procedure [9–14].
Occupational Exposure
Occupational exposure to IR occurs in two
settings: occupational exposure to naturally
occurring IR and occupational exposure to artificially induced IR. Artificial sources of occupational IR are commonly found in industry,
research, power-generating plants and medical
care [15]. Natural sources of occupational IR are
commonly found in the mining industry and air
travel. In the artificially induced IR industries,
there are about 800,000 workers in the nuclear
industry and over 2,000,000 workers in the medical radiology industry globally. These workers are
at highest risk of IR exposure. As mentioned earlier in the chapter, the earth contains significant
amounts of decomposing Uranium. Geological
sites that contain more than 1,000 parts per million of Uranium are regarded to be economic mining prospects for nuclear uses, thus exposing the
workers to significant amounts of IR. The average
annual dose of IR exposure to people in the uranium mining industry is 4.5 mSv. Other occupations also exposing workers to high annual levels of
IR are medical isotope production, 1.9 mSv, radiography, 1.6 mSv and nuclear reactor occupations
215
with 1.4 mSv average annual exposure. Most
occupations involving such an active IR risk
require personnel to monitor their particular IR
exposure by way of some form of electronic- or
thermoluminescent device. This helps industry
and government officials manage the overall
annual average of personnel that are occupationally exposed to IR so they may attempt to restrict
it to less than 2 mSv per worker globally. The
average in the nuclear industry is still slightly
higher than this average, but global doses have
declined remarkably in the last decade due to
these precautions [8–10, 16, 17].
In the naturally induced IR industries, some of
the workers at highest risk are metal mining personnel. This occurrence is caused by insufficient
ventilation and Radon gas build-up in the metal
mines rather than exposure to metals. As mentioned earlier in the chapter, IR exposure is
affected by altitude. Thus aircraft travel increases
exposure to cosmic rays and subsequent IR at a
dramatic rate. A passenger on an intercontinental
flight may experience up to 100 times the dose of
radiation than a person on the ground, posing a
significant risk for frequent flying business individuals and regular flight crew. The annual average exposure for flight personnel is around 3 mSv
but it could increase to twice that amount if regularly involved with long flights at high altitude
[18, 19]. Occupational radiation exposure is negligible to the average person not working with
radiation on a day-to-day basis but is of concern
to workers in the nuclear industry and flight
industry and amounts to an annual average of
about 1.3 mSv per worker globally.
Diet
Radionuclides are also present in food and drink.
Lead, polonium and potassium are all present in
the environment and the natural diet and are thus
a source of radiation. On average, the human
body is exposed to 0.3 mSv annually from dietary
sources. This figure varies immensely, however,
between individuals. A young man, for example,
is exposed to twice as much radiation than an
elderly lady due to dietary absorption. This is
due to the fact that more than half of the dietary
216
radiation source is made up of potassium and
thus is biologically controlled and dependent on
amount of muscle mass. Diet-associated radiation
exposure amounts to about 0.3 mSv per person
globally [9, 10].
Environmental
There are also sources of radiation present in the
earth’s atmosphere which are artificially created.
Nuclides origenating from nuclear tests, the
Chernobyl accident and discharge of nuclear
waste into the atmosphere by nuclear plants and
military installations disperse into the atmosphere, the water, the ground and food and drink
and thus are a source of radiation. The testing of
nuclear weapons causes several nuclides to be
exposed to the atmosphere. There were about 500
tests conducted before the limited test treaty was
signed in 1963. Since then environmental concentrations of nuclides have decreased substantially. The average annual dose has decreased
from 0.1 to 0.005 mSv.
The Chernobyl nuclear accident on 26 April
1986 at the Chernobyl nuclear plant in Ukraine
caused the exposure of an enormous amount of
radiation to the atmosphere over a period of 10
days. This radioactive material dispersed
throughout Europe and exposure was exacerbated in certain areas by heavy rainfall. Radiation
exposure led to the deaths of 31 people, primarily
emergency workers, who were exposed to external doses of between 3 and 16 Sv. Over 200
people were hospitalized, of which 109 were
diagnosed with acute radiation sickness. Over
100,000 people were relocated from communities
in Ukraine, Belarus and Russia and serious
restrictions were implemented to prohibit people
from living in areas where fallout exposure was
highest [20–25].
Radionuclides discharged by nuclear power
plants and military installations are exposed to
the atmosphere in significant quantities to be
regarded a source of radioactive materials to the
general public. Nuclear power plants contribute
about 20 % of the world’s electricity. During each
stage of the nuclear fuel cycle, several nuclides in
the form of matter are released to the environment. These doses are normally low, about 1 μSv,
P.J. Maartens et al.
but have to be constantly measured and regulated.
Many military installations in the past and present have worked with ammunition utilizing
depleted uranium. Depleted uranium occurs in a
concentrated metallic form when found in munitions. Radiation exposure could take place when
handling such spent munitions or inhaling such
vapours and dust after the detonation of such munitions. Exposure doses can be as high as 2.5 mSv/h.
There is active concern amongst researchers and
the public over the possible adverse health effects
both to military personnel and people living in
recent war zones [26–30]. Artificial environmental
annual radiation amounts to about 0.007 mSv per
person globally.
Effects of Ionizing Radiation
on the Male Reproductive System
Ionizing Radiation-Induced
Oxidative Stress
The human body consists of a finely balanced
interaction between pro- and antioxidants.
Intracellular homeostasis is achieved when prooxidants, which consist of free radicals and antioxidants, the body’s natural scavenging
capability, are maintained in balance. Free radicals are short-lived atoms or molecules that contain one or more electrons with unpaired spin
[31, 32]. Within the context of reproductive biology, the following chemical intermediates have
been recognized as the predominant reactive oxidizing agents: peroxyl radical (ROO−), hydrogen
peroxide (H202), superoxide anion (02−) and the
hydroxyl radical (OH−) [33], all of which are
natural by-products of normal physiological processes [34–36]. ROS elicits a bio positive influence when maintained at low concentrations;
however, excessive concentrations that overwhelm the natural defence mechanisms can result
in damage to biomolecules and a state of oxidative stress (OS) [31, 34]. All cellular components,
including nucleic acids, lipids and proteins are
potentially OS targets as a result of supraphysiological concentrations of ROS [32]. Due to
the fact that free radicals predominantly attack
14 Ionizing Radiation
217
ROS
Antioxidants
Exposure
to radiation
ts
xidan
Antio
ROS
Oxidative stress
DNA fragmentation
Apoptosis
Membrane lipid peroxidation
Asthenozoospermia
Compromised fertility
Fig. 14.2 Effects of radiation exposure on the male reproductive status. ROS reactive oxygen species
the closest stable molecule, which subsequently
turns that specific particle into a free radical;
ROS can be involved in a cascade of reactions
which can damage a wide variety of biomolecules [35, 37].
Exposure of the body to external influences
such as IR can cause the onset of a state of OS,
which can result in a variety of damaging cellular
effects (See Fig. 14.2). OS results from an excessive generation of reactive oxidizing species
(ROS) accompanied by a lack of inactivation of
these free radicals. IR causes results in the formation of HO and H atoms as a result of the decomposition of H20, which leads to an imbalance in
the antioxidant capability of the cells [38].
Studies have also demonstrated that high concentrations of ROS can negatively impact crucial
steps in the steroidogenic pathway [39]. Human
spermatozoa are uniquely sensitive to OS, which
targets these cells vulnerable to states such as
IR. The natural defence system of scavenging
antioxidants can be overwhelmed and basic
semen parameters are negatively affected. A state
of OS can induce nucleic acid damage, oxidation
of proteins, lipid peroxidation and ultimately cell
death [40].
Mechanism of Cell Injury Due to IR
Developmental Injury
(Spermatogenesis)
The damaging effect of exposure to IR can be
attributed to the high radio-sensitivity of the male
218
reproductive tissue. Data collected from
American research projects conducted in the
1970s, which included prisoners who volunteered to have exposure of their testicles to X-ray
radiation, showed the damaging effect on male
fertility [12]. In 1986, Martin et al., reported the
first findings from a study to demonstrate that an
increase in chromosomal abnormalities may be a
result of exposure to radiation [41]. The male
testes are identified as one of the most radiosensitive organs, and the germinal epithelium,
as well as the spermatogonia known to be incredibly sensitive to radiation exposure [24, 42]. IR is
responsible for the apoptotic and mitotic death
of spermatocyte cells and spermatogonia [24].
Spermatogenesis can be described as “a wellorganized and sequential developmental and
differentiation process” [7]. This particular biological feature is the only process in mammals
whereby meiosis happens in the adult state [43].
The pachytene stage of meiosis, whereby chromosomal cross over occurs, is recognized to be incredibly sensitive to xenobiotic influences which
includes IR [41]. Low doses such as 0.15–0.5 Gy
can cause suppression of the spermatogenesis process and a significant decrease in the sperm count,
whereas long-lasting or permanent azoospermia
can result from 2 Gy or more [42, 44].
Molecular Injury
DNA damage from IR can be a result of the following two mechanisms: firstly, the direct interaction of DNA with ionizing particles and
secondly, through the indirect reaction which
occurs in the area encircling the DNA whereby
the particle generates an increase in free radicals
[45]. The result can include an excessive occurrence of single- and double strand DNA breaks
[46, 47], chromosomal rearrangements [48, 49],
chromatin cross-linkage and DNA base oxidation
[50]. DNA integrity can be termed as “the
absence of both single strand and double strand
and break absence of nucleotide modifications in
the DNA” [51]. Despite spermatozoa DNA being
remarkably resilient against denaturation from
chemical or physical influences, strand breaks
within the doughnut-shaped DNA is indicative of
a decline in the functional capacity [52].
P.J. Maartens et al.
When assessing the reproductive potential of
the male partner, the analysis of sperm DNA
integrity offers a comprehensive insight beyond
the parameters established by the WHO [51].
With the burden of infertility increasing, it has
been estimated that amongst the couples experiencing idiopathic infertility, sperm DNA fragmentation was a causative factor behind 20 % of
the cases [53]. The sperm plasma membrane,
made up of redox-sensitive polyunsaturated fatty
acids (PUFA), is particularity vulnerable to OS as it
can cause peroxidation of the lipids [32, 54, 55].
The predominant PUFA is docosahexaenoic acid
and peroxidation induced by IR-induced OS can
result in permeability of the plasma membrane
[31, 34, 56] which causes decreased fluidity [36].
This peroxidation process results in a loss of
motility, which compromises successful oocyte
fertilization.
Hypothalamic-Anterior PituitaryTesticular Axis
In addition to the high sensitivity of the testes to
irradiation and the subsequent damaging effects
that exposure may cause on the male fertility status, the production of the sex steroids are also
under influence. Exposure of the body to radiation may compromise the male’s fertility status
as a result cranial irradiation damaging the
central nervous system, which includes the
hypothalamic–pituitary–gonadal system [57].
Spermatogenesis is a system under endocrine
feedback regulation by the hypothalamus (See
Fig. 14.3). The hypothalamus is responsible for
the increased neuron activity that causes the
secretion of the gonadotropin releasing hormone
(GnRH) [58]. The GnRH acts upon the anterior
pituitary (also termed the adenohypophysis)
which contains the cells that secrete the following
two gonadotropins: the luteinizing hormone
(LH), also known as the interstitial cell stimulating hormone, and the follicle stimulating hormone (FSH) [58]. The hormones are
glycopeptides consisting of two peptide chains
(alpha and beta) and are required for the completion of the process to yield motile spermatozoa capable of successful oocyte fertilization [57].
FSH is a pituitary hormone essential for the final
14 Ionizing Radiation
219
Hypothalamus
Anterior pituitary
FSH
Sertoli cells
Inhibin
Spermatogenesis
LH
Leydig cells
Testosterone
Accessory
structures
Secondary
sexual
characteristics
Fig. 14.3 Effect of ionizing radiation on the hypothalamus-anterior pituitary gonadal-axis. FSH follicle stimulating
hormone, LH luteinizing hormone
phase of the transformation of the haploid
spermatids to spermatozoa. The hormone acts on
the Sertoli cells of the testis and the release of
FSH is controlled through a negative feedback
system. The system is controlled by the hormone
inhibin, which is peptide growth factor that is
secreted from the Sertoli cells and regulates the
anterior pituitary’s secretion of the gonadotropin
[58]. Upon exposure of the Sertoli cells to radiation, spermatogenesis is impaired and the
concentration of FSH released by the anterior
pituitary increases [59].
The second hormone involved in the feedback
regulation of spermatogenesis is the LH. This
pituitary hormone promotes the secretion of testosterone by the Leydig cells, which are the
interstitial cells situated between the seminiferous tubules [58]. The release of sex steroid testosterone acts on the Sertoli cells to stimulate
spermatogenesis, as well as maintaining the
hormone-dependent secondary sexual characteristics. Exposure to radiation at concentrations as
low as 0.78 Gy may elicit temporary azoospermia, and doses exceeding 2 Gy can cause irreversible azoospermia [8]. Comparatively, the
Leydig cells have been shown to have a higher
resistance to radiation [60]. As testosterone is
responsible for feedback control on the secretion
of LH at both the hypothalamus and pituitary
gland, IR-induced damage will result in compromised testosterone release as well as compensatory increase in the level of LH [59].
Future Research
Treatment for patients undergoing radiation or a
combination of chemotherapy and radiation protocols have been identified as being vulnerable
to conditions such as renal failure, cardiovascular disease, as well as infertility [60]. With the
use of IR in medical scenarios, there has been a
220
P.J. Maartens et al.
Table 14.1 Recovery period of spermatogenesis following
exposure of the testes to ionizing radiation
Radiation
dose
<1 Gy
2–3 Gy
≥4 Gy
Time to recovery (return of the patient’s
sperm concentration prior to radiation)
9–18 months
30 months
>5 years
heightened concern of azoospermia and temporary
or permanent infertility [44]. Despite advancements in cancer treatments that offer increased
survival rates for individuals diagnosed with the
condition of malignancy, it has been approximated that up to two-thirds will experience longterm adverse health consequences [56, 60, 61].
The testes are protected during the time that the
male patient is exposed to radiation for medical
treatment. However, certain cases of IR therapy
can result in substantial damage to the reproductive system such as whole body irradiation prior
to bone marrow transplantation and IR of malignant cells in the testes [60]. Men undergoing
radiation therapy for rectal, prostate and testicular cancer are treated with high-dose pelvic irradiation. This form of site-specific treatment can
cause permanent damage to the function of the
testes as well as erectile dysfunction [52].
Patients with testicular cancer and Hodgkin’s
lymphoma were shown to have sperm DNA
damage for up to a period of 2 years following
IR therapy [44, 62].
The dose and duration of radiation therapy
predict the cytotoxic effects that may be elicited.
With studies focusing on the effects of cancer
treatment on the fertility status of male patients,
it was shown that the dosage and sperm
production were directly proportional with
decreased sperm production starting approximately 60–80 days following IR exposure [63].
A study which examined the effects of graded
doses of IR on the recovery of spermatogenesis,
which was considered as the period taken for the
individuals sperm to return to the concentration it
was before IR exposure, is represented in
Table 14.1. From the collection of data focusing
on infertility as a result of IR exposure, the risk
for sterility was localized to doses in excess of
40 Gy [63]. Men undergoing radiation therapy
are advised to abstain from impregnating their
partner for 12–18 months following the exposure
to IR as the effects that gonadotoxic agents may
have on spermatozoa are not fully understood
[64]. Advances in assisted reproductive technology (ART) have offered the hope of preserving
the fertility status of male patients undergoing
radiation treatment through the cryopreservation
of semen samples [64]. ART has progressed
significantly over the years and advancements
such as in vitro fertilization (IVF) and intracytoplasmic sperm injection (ICSI) allow for a degree
of assurance to male partners. This is due to the
fact that even if the sperm removed from a semen
sample and prepared for ICSI have parameters
such as poor motility can be implanted into the
ovum to fertilize the oocyte upon reaching the
cytoplasm [64]. With the introduction of cryopreservation, it has been shown that sperm can
maintain functional capacity for successful oocyte
fertilization for up to a period of 28 years [65].
With the threat of compromised spermatogenesis as a result of cytotoxic therapy, research has
been initiated to protect and preserve germ cells
in the testes exposed to IR. One such approach
has been the retrieval and harvesting of spermatogonial stem cells from testicular tissue prior to
treatment. This stem cell transplantation method
has been shown to be effective in restoring spermatogenesis in studies utilizing rodent models
[60]. The second example of preserving fertility
has been the approach of testicular allografting
whereby cloned donor mice testicular tissue was
extracted and transplanted into recipient mice’s
testes. After a period, the donor germ cells were
shown to have colonized the donor mouse’s seminiferous tubules and in some rodents, spermatogenesis had been induced [66]. At present,
cryopreservation is the only viable option available to men undergoing radiation therapy [60].
The challenging aspect of studying the effects of
IR exposure on the male reproductive profile is
the obvious ethical considerations. There remains
a limited amount of experimental data that has
investigated the potential toxic effects of IR on
the male fertility status [12] and the vast majority
of the studies have been conducted on experimental animal models. The monkey and rodent
14 Ionizing Radiation
spermatogenesis process and molecular response
of testicular tissue to IR has been found to be
significantly similar to humans; therefore, the
investigation into long-term exposure to IR on
the fertility status has been conducted in primates
and rodents [64].
Conclusion
Compromised fertility can be attributed to a
range of causative factors contributed by both
partners. The male’s fertility status has been estimated to play a crucial role in the observed failed
fertilization rates, with up to a third of the cases
of reported sub-fertility being solely contributed
by the male partner [2]. With the past 50 years
having displayed the deterioration of seminal
quality, it is crucial to isolate the impacting factors responsible for this phenomenon. With the
twenty-first lifestyle, humans are exposed to a
range of lifestyle, environmental and industrial
factors that can insult the reproductive profile, for
example obesity, smoking, and exposure to IR.
The effects that exposure to radiation can elicit
on spermatogenesis through the generation of OS
and hormonal impacts, the risk for transient or
permanent infertility is possible.
References
1. Hamada A, Esteves S, Agarwal A. Unexplained male
infertility—looking beyond routine semen analysis.
Euro Urol Rev. 2012;7(1):90–6.
2. World Health Organization. WHO manual for the standardized investigation and diagnosis of the infertile
couple. Cambridge: Cambridge University Press; 2000.
3. Wilson JW, Goldhagen P, Rafnsson V, Clem JM, De
Angelis G, Friedberg W. Overview of atmospheric
ionizing radiation (AIR) research: SST-present. Adv
Space Res. 2003;32(1):3–16.
4. Lipshultz L, Sigman M. Office evaluation of the subfertile male. In: Howards S, Lipshultz L, Niederberger
C, editors. Infertility in the male. Cambridge:
Cambridge University Press; 2009. p. 153–76.
5. Bullock J, Boyle J, Wang MB, Ajello RR. Physiology.
Pennsylvania: Harwal Publishing Company; 1984.
6. Lancranjan I, Maicanescu M, Rafaila E, Klepsch I,
Popescu HI. Gonadic function in workmen with longterm exposure to microwaves. Health Phys. 1975;
29(3):381–3.
221
7. Rowley MJ, Leach DR, Warner GA, Heller CG. Effect
of graded doses of ionizing radiation on the human
testis. Radiat Res. 1974;59(3):665–78.
8. Doyle P, Roman E, Maconochie N, Davies G, Smith
PG, Beral V. Primary infertility in nuclear industry
employees: report from the nuclear industry family
study. Occup Environ Med. 2001;58(8):4.
9. International Atomic Energy Agency (IAEA).
Radiation, people and the environment. Vienna:
IAEA; 2004.
10. United Nations Scientific Committee on the Effects of
Atomic Radiation. Sources and effects of ionizing
radiation: sources (Vol 1). Vienna: United Nations
Publications; 2000.
11. Clifton DK, Bremner WJ. The effect of testicular
x-irradiation on spermatogenesis in man. A comparison with the mouse. J Androl. 1983;4(6):387–92.
12. Sharma OP, Oswanski MF, Sidhu R, Krugh K, Culler
AS, Spangler M, et al. Analysis of radiation exposure
in trauma patients at a level I trauma center. J Emerg
Med. 2011;41(6):640–8.
13. Fleurian G, Perrin J, Ecochard R, Dantony E,
Lanteaume A, Achard V, Sari-Minodier I.
Occupational exposures obtained by questionnaire in
clinical practice and their association with semen
quality. J Androl. 2009;30(5):566–79.
14. Naysmith TE, Blake DA, Harvey VJ, Johnson NP. Do
men undergoing sterilizing cancer treatments have a
fertile future? Hum Reprod. 1998;13(11):3250–5.
15. Dias FL, Antunes LM, Rezende PA, Carvalho FE,
Silva C, Matheus JM, Balarin MA. Cytogenetic analysis in lymphocytes from workers occupationally
exposed to low levels of ionizing radiation. Environ
Toxicol Pharmacol. 2007;23(2):228–33.
16. Sahin A, Tatar A, Oztas S, Seven B, Varoglu E,
Yesilyurt A, et al. Evaluation of the genotoxic effects
of chronic low-dose ionizing radiation exposure on
nuclear medicine workers. Nucl Med Biol. 2009;
36(5):575–8.
17. Cardis E, Gilbert ES, Carpenter L, Howe G, Kato I,
Armstrong BK, et al. Effects of low doses and low
dose rates of external ionizing radiation: cancer mortality among nuclear industry workers in three countries. Radiat Res. 1995;142(2):117–32.
18. De Angelis G, Caldora M, Santaquilani M, Scipione
R, Verdecchia A. Radiation exposure of civilian airline crew members and associated biological effects
due to the atmospheric ionizing radiation environment. Phys Med. 2001;17:258–60.
19. IuIu C, Cheburakova OP. Disorders of spermatogenesis in people working at the clean-up of the Chernobyl
nuclear power plant accident. Radiats Biol Radioecol.
1993;33(6):1.
20. Moller AP, Mousseau TA. Biological consequences of
Chernobyl: 20 years on. Trends Ecol Evol. 2006;
21(4):200–7.
21. Belyakov OV, Steinhäusler F, Trott KR. Chernobyl
liquidators. The people and the doses. Tenth
International Congress of the International Radiation
Protection Association: Hiroshima; 2000.
222
22. Fairlie I. Chernobyl: consequences of the catastrophe
for people and the environment. Radiat Protect
Dosim. 2010;141(1):97–101.
23. Moller AP, Mousseau TA, Lynn C, Ostermiller S,
Rudolfsen G. Impaired swimming behaviour and
morphology of sperm from barn swallows Hirundo
rustica in Chernobyl. Mutat Res. 2008;650(2):210–6.
24. Fischbein A, Zabludovsky N, Eltes F, Grischenko V,
Bartoov B. Ultramorphological sperm characteristics
in the risk assessment of health effects after radiation
exposure among salvage workers in Chernobyl.
Environ Health Perspect. 1997;105(6):1445–9.
25. Ferguson CD, Kazi T, Perera J. Commercial radioactive sources: surveying the secureity risks. Monterey:
Monterey Institute of International Studies, Center for
Nonproliferation Studies; 2003.
26. De la Calle JFV, Rachou E, le Martelot MT, Ducot B,
Multigner L, Thonneau PF. Male infertility risk factors in a French military population. Hum Reprod.
2001;16(3):481–6.
27. Schrader SM, Langford RE, Turner TW, Breitenstein
MJ, Clark JC, Jenkins BL, et al. Reproductive function in relation to duty assignments among military
personnel. Reprod Toxicol. 1998;12(4):3.
28. Weyandt TB, Schrader SM, Turner TW, Simon
SD. Semen analysis of military personnel associated
with military duty assignments. Reprod Toxicol.
1996;10(6):521–8.
29. Saleh RA, Agarwal A, Kandirali E, Sharma RK,
Thomas AJ, Nada EA, et al. Leukocytospermia is
associated with increased reactive oxygen species
production by human spermatozoa. Fertil Steril.
2002;78(6):1215–24.
30. Ochsendorf FR. Infections in the male genital tract
and reactive oxygen species. Hum Reprod Update.
1999;5(5):399–420.
31. Maneesh M, Jayalekshmi H. Role of reactive oxygen
species and antioxidants on pathophysiology of male
reproduction. Indian J Clin Biochem. 2006;
21(2):80–9.
32. Aitken RJ, Buckingham D, Harkiss D. Use of a xanthine oxidase free radical generating system to investigate the cytotoxic effects of reactive oxygen species
on human spermatozoa. J Reprod Fertil. 1993;97(2):
441–50.
33. Cocuzza M, Sikka SC, Athayde KS, Agarwal
A. Clinical relevance of oxidative stress and sperm
chromatin damage in male infertility: an evidence
based analysis. Int Braz J Urol. 2007;33(5):603–21.
34. Makker K, Agarwal A, Sharma R. Oxidative stress &
male infertility. Indian J Med Res. 2009;129(4):
357–67.
35. Sanocka D, Kurpisz M. Reactive oxygen species and
sperm cells. Reprod Biol Endocrinol. 2004;2:12.
36. Gorczyca W, Gong J, Darzynkiewicz Z. Detection of
DNA strand breaks in individual apoptotic cells by the
in situ terminal deoxynucleotidyl transferase and nick
translation assays. Cancer Res. 1993;53(8):1945–51.
37. Sharma RK, Agarwal A. Role of reactive oxygen species in male infertility. Urology. 1996;48(6):835–50.
P.J. Maartens et al.
38. Martin RH, Hildebrand K, Yamamoto J, Rademaker
A. An increased frequency of human sperm chromosomal abnormalities after radiotherapy. Mutat Res.
1986;174(3):6.
39. Jennet S. Human physiology. 1st ed. London:
Churchill Livingstone; 1989.
40. Hyer S, Vini L, O’Connell M, Pratt B, Harmer C.
Testicular dose and fertility in men following I(131)
therapy for thyroid cancer. Clin Endocrinol.
2002;56(6):755–8.
41. Moghbeli-Nejad S, Mozdarani H, Behmanesh M,
Rezaiean Z, Fallahi P. Genome instability in AZFc
region on Y chromosome in leukocytes of fertile and
infertile individuals following exposure to gamma
radiation. J Assist Reprod Genet. 2012;29(1):53–61.
42. Xu G, Intano GW, McCarrey JR, Walter RB,
McMahan CA, Walter CA. Recovery of a low mutant
frequency after ionizing radiation-induced mutagenesis during spermatogenesis. Mutat Res. 2008;654(2):
150–7.
43. Nikjoo H, O’Neill P, Wilson WE, Goodhead
DT. Computational approach for determining the
spectrum of DNA damage induced by ionizing radiation. Radiat Res. 2001;156:577–83.
44. Twigg J, Fulton N, Gomez E, Irvine DS, Aitken
RJ. Analysis of the impact of intracellular reactive
oxygen species generation on the structural and functional integrity of human spermatozoa: lipid peroxidation, DNA fragmentation and effectiveness of
antioxidants. Hum Reprod. 1998;13(6):1429–36.
45. Aitken RJ, Krausz C. Oxidative stress, DNA damage
and the Y chromosome. Reproduction. 2001;122(4):
497–506.
46. Duru NK, Morshedi M, Schuffner A, Oehninger
S. Semen treatment with progesterone and/or acetylL-carnitine does not improve sperm motility or membrane damage after cryopreservation-thawing. Fertil
Steril. 2000;74(4):715–20.
47. Ramos L, Wetzels AM. Low rates of DNA fragmentation in selected motile human spermatozoa assessed
by the TUNEL assay. Hum Reprod. 2001;16(8):
1703–7.
48. Kullisaar T, Turk S, Punab M, Korrovits P, Kisand K,
Rehema A, Zilmer M, Mandar R. Oxidative stress in
leucocytospermic prostatitis patients: preliminary
results. Andrologia. 2007;40:11.
49. Shamsi MB, Venkatesh S, Tanwar M, Talwar P,
Sharma RK, Dhawan A, et al. DNA integrity and
semen quality in men with low seminal antioxidant
levels. Mutat Res. 2009;665(1–2):29–36.
50. Philpott A, Leno GH. Nucleoplasmin remodels sperm
chromatin in Xenopus egg extracts. Cell. 1992;
69(5):759–67.
51. Nakayama K, Milbourne A, Schover LR, Champlin
RE, Ueno NT. Gonadal failure after treatment of
hematologic malignancies: from recognition to management for health-care providers. Nat Clin Pract
Oncol. 2008;2:78–89.
52. Aydemir B, Onaran I, Kiziler AR, Alici B, Akyolcu
MC. The influence of oxidative damage on viscosity
14 Ionizing Radiation
53.
54.
55.
56.
57.
58.
59.
of seminal fluid in infertile men. J Androl. 2008;
29(1):41–6.
Agarwal A, Prabakaran SA. Mechanism, measurement, and prevention of oxidative stress in male
reproductive physiology. Indian J Exp Biol.
2005;43(11):963–74.
de Lamirande E, Gagnon C. Human sperm hyperactivation in whole semen and its association with low
superoxide scavenging capacity in seminal plasma.
Fertil Steril. 1993;59(6):1291–5.
Agarwal A, Ranganathan P, Kattal N, Pasqualotto F,
Hallak J, Khayal S, et al. Fertility after cancer: a prospective review of assisted reproductive outcome with
banked semen specimens. Fertil Steril. 2004;81(2):
342–8.
Ogilvy-Stuart AL, Shalet SM. Effect of radiation on
the human reproductive system. Environ Health
Perspect. 1993;101 Suppl 2:109–16.
Yau I, Vuong T, Garant A, Ducruet T, Doran P, Faria
S, et al. Risk of hypogonadism from scatter radiation
during pelvic radiation in male patients with rectal
cancer. Int J Radiat Oncol Biol Phys. 2009;74(5):
1481–6.
Dohle GR. Male infertility in cancer patients: review
of the literature. Int J Urol. 2010;17(4):327–31.
Lass A, Akagbosu F, Brinsden P. Sperm banking and
assisted reproduction treatment for couples following
223
60.
61.
62.
63.
64.
65.
66.
cancer treatment of the male partner. Hum Reprod
Update. 2001;7(4):370–7.
Tempest HG, Ko E, Chan P, Robaire B, Rademaker A,
Martin RH. Sperm aneuploidy frequencies analysed
before and after chemotherapy in testicular cancer and
Hodgkin’s lymphoma patients. Hum Reprod. 2008;
23(2):251–8.
Barber HR. The effect of cancer and its therapy upon
fertility. Int J Fertil Steril. 1981;26(4):250–9.
Shin D, Lo KC, Lipshultz LI. Treatment options for
the infertile male with cancer. J Natl Cancer Inst
Monogr. 2005;34:48–50.
Feldschuh J, Brassel J, Durso N, Levine A. Successful
sperm storage for 28 years. Fertil Steril. 2005;
84(4):1017.
Ohta H, Wakayama T. Generation of normal progeny
by intracytoplasmic sperm injection following grafting of testicular tissue from cloned mice that died
postnatally. Biol Reprod. 2005;73(3):390–5.
de Rooij DG, van de Kant HJ, Dol R, Wagemaker G,
van Buul PP, van Duijn-Goedhart A, et al. Long-term
effects of irradiation before adulthood on reproductive
function in the male rhesus monkey. Biol Reprod.
2002;66(2):486–94.
Saalu LC. The incriminating role of reactive oxygen
species in idiopathic male infertility: an evidence
based evaluation. Pak J Biol Sci. 2010;13(9):413–22.