Vol. 1 - Pages 9.1-9.30 (Printed Version)
Reproductive System
REPRODUCTIVE SYSTEM:
INTRODUCTION
Lowell E. Sever
Male and female reproductive toxicity are topics of
increasing interest in consideration of occupational health hazards. Reproductive toxicity has been defined
as the occurrence of adverse effects on the reproductive system that may result
from exposure to environmental agents. The toxicity may be expressed as
alterations to the reproductive organs and/or the related endocrine system. The
manifestations of such toxicity may include:
·
alterations in sexual behaviour
·
reduced fertility
·
adverse pregnancy outcomes
·
modifications of other functions that are dependent on
the integrity of the reproductive system.
Mechanisms underlying reproductive toxicity are
complex. More xenobiotic substances have been tested and demonstrated to be
toxic to the male reproductive process than to the female. However, it is not
known whether this is due to underlying differences in toxicity or to the
greater ease of studying sperm than oocytes.
Developmental Toxicity
Developmental toxicity has been defined as the
occurrence of adverse effects on the developing organism that may result from
exposure prior to conception (either parent), during prenatal development or
postnatally to the time of sexual maturation. Adverse developmental effects may
be detected at any point in the life span of the organism. The major
manifestations of developmental toxicity include:
·
death of the developing organism
·
structural abnormality
·
altered growth
·
functional deficiency.
In the following discussion, developmental toxicity will be used as an all-inclusive term to
refer to exposures to the mother, father or conceptus that lead to abnormal
development. The term teratogenesis
will be used to refer more specifically to exposures to the conceptus which
produce a structural malformation. Our discussion will not include the effects
of postnatal exposures on development.
Mutagenesis
In addition to reproductive toxicity, exposure to
either parent prior to conception has the potential of resulting in
developmental defects through mutagenesis, changes in the genetic material that
is passed from parent to offspring. Such changes can occur either at the level
of individual genes or at the chromosomal level. Changes in individual genes
can result in the transmission of altered genetic messages while changes at the
chromosomal level can result in the transmission of abnormalities in
chromosomal number or structure.
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It is interesting that some of the strongest evidence
for a role for preconception exposures in developmental abnormalities comes
from studies of paternal exposures. For example, Prader-Willi syndrome, a birth
defect characterized by hypotonicity in the newborn period and, later, marked
obesity and behaviour problems, has been associated with paternal occupational
exposures to hydrocarbons. Other studies have shown associations between
paternal preconception exposures to physical agents and congenital
malformations and childhood cancers. For example, paternal occupational
exposure to ionizing radiation has been associated with an increased risk of
neural tube defects and increased risk of childhood leukaemia, and several
studies have suggested associations between paternal preconception occupational
exposure to electromagnetic fields and childhood brain tumours (Gold and Sever
1994). In assessing both reproductive and developmental hazards of workplace
exposures increased attention must be paid to the possible effects among males.
It is quite likely that some defects of unknown
aetiology involve a genetic component which may be related to parental
exposures. Because of associations demonstrated between father’s age and
mutation rates it is logical to believe that other paternal factors and
exposures may be associated with gene mutations. The well-established
association between maternal age and chromosomal non-disjunction, resulting in
abnormalities in chromosomal number, suggests a significant role for maternal
exposures in chromosomal abnormalities.
As our understanding of the human genome increases it
is likely that we will be able to trace more developmental defects to mutagenic
changes in the DNA of single genes or structural changes in portions of
chromosomes.
Teratogenesis
The adverse effects on human development of exposure
of the conceptus to exogenous chemical agents have been recognized since the
discovery of the teratogenicity of thalidomide in 1961. Wilson (1973) has
developed six “general principles of teratology” that are relevant to this discussion.
These principles are:
1. The final
manifestations of abnormal development are death, malformation, growth
retardation and functional disorder.
2. Susceptibility
of the conceptus to teratogenic agents varies with the developmental stage at
the time of exposure.
3. Teratogenic
agents act in specific ways (mechanisms) on developing cells and tissues in
initiating abnormal embryogenesis (pathogenesis).
4. Manifestations
of abnormal development increase in degree from the no-effect to the totally
lethal level as dosage increases.
5. The access
of adverse environmental influences to developing tissues depends on the nature
of the agent.
6. Susceptibility
to a teratogen depends on the genotype of the conceptus and on the manner in
which the genotype interacts with environmental factors.
The first four of these principles will be discussed
in further detail, as will the combination of principles 1, 2 and 4 (outcome,
exposure timing and dose).
Spectrum of Adverse Outcomes
Associated with Exposure
There is a spectrum of adverse outcomes potentially
associated with exposure. Occupational studies that focus on a single outcome
risk overlooking other important reproductive effects.
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Figure 9.1 [REP01FE] lists some examples of
developmental outcomes potentially associated with exposure to occupational
teratogens. Results of some occupational studies have suggested that congenital
malformations and spontaneous abortions are associated with the same
exposures—for example, anaesthetic gases and organic solvents.
Spontaneous abortion is an important outcome to
consider because it can result from different mechanisms through several
pathogenic processes. A spontaneous abortion can be the result of toxicity to
the embryo or foetus, chromosomal alterations, single gene effects or morphological
abnormalities. It is important to try to differentiate between karyotypically
normal and abnormal conceptuses in studies of spontaneous abortions.
Timing of Exposure
Wilson’s second principle relates susceptibility to
abnormal development to the time of exposure, that is, the gestational age of
the conceptus. This principle has been well established for the induction of
structural malformations, and the sensitive periods for organogenesis are known
for many structures. Considering an expanded array of outcomes, the sensitive
period during which any effect can be induced must be extended throughout
gestation.
In assessing occupational developmental toxicity,
exposure should be determined and classified for the appropriate critical
period—that is, gestational age(s)—for each outcome. For example, spontaneous
abortions and congenital malformations are likely to be related to first and
second trimester exposure, whereas low birth weight and functional disorders
such as seizure disorders and mental retardation are more likely to be related
to second and third trimester exposure.
Teratogenic Mechanisms
The third principle is the importance of considering
the potential mechanisms that might initiate abnormal embryogenesis. A number
of different mechanisms have been suggested which could lead to teratogenesis
(Wilson 1977). These include:
·
mutational changes in DNA sequences
·
chromosomal abnormalities leading to structural or
quantitative changes in DNA
·
alteration or inhibition of intracellular metabolism,
e.g., metabolic blocks and lack of co-enzymes, precursors or substrates for
biosynthesis
·
interruption of DNA or RNA synthesis
·
interference with mitosis
·
interference with cell differentiation
·
failure of cell-to-cell interactions
·
failure of cell migrations
·
cell death through direct cytotoxic effects
·
effects on cell membrane permeability and osmolar
changes
·
physical disruption of cells or tissues.
By considering mechanisms, investigators can develop
biologically meaningful groupings of outcomes. This can also provide insight
into potential teratogens; for example, relationships between carcinogenesis,
mutagenesis and teratogenesis have been discussed for some time. From the
perspective of assessing occupational reproductive hazards, this is of
particular importance for two distinct reasons: (1) substances that are
carcinogenic or mutagenic have an increased probability of being teratogenic,
suggesting that particular attention should be paid to the reproductive effects
of such substances, and (2) effects on deoxyribonucleic acid (DNA), producing
somatic mutations, are thought to be mechanisms for both carcinogenesis and
teratogenesis.
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Dose and Outcome
The fourth principle concerning teratogenesis is the
relationship of outcome to dose. This principle is clearly established in many
animal studies, and Selevan (1985) has discussed its potential relevance to the
human situation, noting the importance of multiple reproductive outcomes within
specific dose ranges and suggesting that a dose-response relationship could be
reflected in an increasing rate of a particular outcome with increasing dose
and/or a shift in the spectrum of the outcomes observed.
In regard to teratogenesis and dose, there is
considerable concern about functional disturbances resulting from the possible
behavioural effects of prenatal exposure to environmental agents. Animal
behavioural teratology is expanding rapidly, but human behavioural
environmental teratology is in a relatively early stage of development. At
present, there are critical limitations in the definition and ascertainment of
appropriate behavioural outcomes for epidemiological studies. In addition it is
possible that low-level exposures to developmental toxicants are important for
some functional effects.
Multiple Outcomes and Exposure
Timing and Dose
Of particular importance with respect to the
identification of workplace developmental hazards are the concepts of multiple
outcomes and exposure timing and dose. On the basis of what we know about the
biology of development, it is clear that there are relationships between
reproductive outcomes such as spontaneous abortion and intrauterine growth
retardation and congenital malformations. In addition, multiple effects have
been shown for many developmental toxicants (Table 9.1 [REP01TE]).
Relevant to this are issues of exposure timing and
dose-response relationships. It has long been recognized that the embryonic
period during which organogenesis occurs (two to eight weeks post-conception)
is the time of greatest sensitivity to the induction of structural
malformations. The foetal period from eight weeks to term is the time of
histogenesis, with rapid increase in cell number and cellular differentiation
occurring during this time. It is then that functional abnormalities and growth
retardation are most likely to be induced. It is possible that there may be
relationships between dose and response during this period where a high dose
might lead to growth retardation and a lower dose might result in functional or
behavioural disturbance.
Male-Mediated Developmental
Toxicity
While developmental toxicity is usually considered to
result from exposure of the female and the conceptus—that is, teratogenic
effects—there is increasing evidence from both animal and human studies for
male-mediated developmental effects. Proposed mechanisms for such effects
include transmission of chemicals from the father to the conceptus via seminal
fluid, indirect contamination of the mother and the conceptus by substances
carried from the workplace into the home environment through personal
contamination, and—as noted earlier—paternal preconception exposures that
result in transmissible genetic changes (mutations).
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