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Birnbaum, LS and SE Fenton. 2002. Cancer And Developmental
Exposure to Endocrine Disruptors. Environmental Health
Perspectives
doi:10.1289/ehp.5686.
Birnbaum and Fenton review a wide array of experimental evidence from
animals showing that exposure to endocrine-disrupting compounds
in early development can cause cancer and/or increase
sensitivity to cancer-causing agents later in life.
Their review then highlights how few human studies have been built upon
this understanding. Almost all human epidemiological research
into cancer risk from contaminant exposures examines chemical levels
only at the time of diagnosis or afterward. This approach
misses entirely the period of developmental sensitivity to exposures
that animal studies have identified [a recent example
being
the Long Island Breast Cancer study].
Birnbaum and Fenton summarize this with two important questions about
the way most human studies have been conducted:
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"Could we be trying to correlate exposure and effect at the wrong
time? If it is prenatal, or early life stage, exposure that is
critical to disease susceptibility, why are we measuring
environmental chemicals in people once they have developed breast
cancer? The critical exposure window may have been much earlier." |
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One interesting pattern that emerges from their review of animal
experiments is that in utero exposure to several endocrine
disrupting compounds (including dioxin, atrazine and bisphenol A) can
alter mammary gland development in ways that prolong the period of
sensitivity to carcinogens. This suggests a different way of
thinking about the contribution of these contaminants to carcinogenesis:
even if they don't cause cancer directly, they contribute to cancer risk
by increasing vulnerability. No epidemiological study has ever
attempted to test for this sort of effect in people.
Birbaum and Fenton begin their review with a very succinct summary of
the basic reasons why early developmental stages through puberty are
especially vulnerable to chemical exposure:
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The pace of and the nature of change in a developing fetus or child is
dramatically enhanced compared with that in an adult. An embryo and
fetus is changing quickly, with rapid cycles of cell division and
growth, and massive changes in the patterns of gene activation over
time. These cycles provide extensive opportunities for mistakes to
occur and be incorporated into the organism. Sometimes these mistakes
are mutagenic, sometimes they are based on changes outside the genes.
Comparable periods of cell division, differentiation and growth are
long since over in an adult. Hence the chances for mistakes to be made
and incorporated aren't nearly as common in an adult compared to an
embryo or fetus.
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Second, physiological barriers such as the blood-brain barrier are not
yet complete in the womb.
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Finally, the enzymatic mechanisms that work to detoxify contaminants
in adults are not fully developed until after birth.
They then cite two examples offering "unequivocal evidence" from human
studies demonstrating that developmental exposures can cause cancers in
children and young adults. This comes from studies from ionizing
radiation and the synthetic estrogen
diethylstilbestrol.
Studies of a range of other human exposures suggest causal relationships
between developmental exposure and subsequent cancers, but the evidence,
while strong, is not as conclusive as for DES and radiation. These other
studies implicate occupational exposures of parents to brain cancers in
children, pesticides, paints, paint thinners and solvents in causing
leukemia, and cigarette smoke and childhood cancer, among others. In
this discussion Birnbaum and Fenton also comment on one of the chief
obstacles impeding epidemiological studies of childhood cancers:
they are so uncommon in the general population that prospective studies
rarely have a sufficient sample size to find positive results.
Turning to animal studies where experimental studies are possible,
Birnbaum and Fenton observe that "data from experimental animal studies
for developmental exposures and early lifestage or adult cancer is far
more extensive and convincing than the current epidemiological data."
They review an extensive literature showing conclusively that
prenatal and early postnatal exposure to various types of radiation and
to many different chemicals cause cancers later in life in the exposed
animals.
Induced tumors span the gamut: skin carcinogenesis, liver ovarian,
uterine and pituitary tumors from prenatal x-ray exposure; respiratory
tumors from a wide array of mutagens, including ethyl-nitrosourea (ENU);
uterine tumors from ENU, dimethylbenz[a]anthracene (DMBA) and urethane;
nervous system tumors in a wide range of mammalian species from ENU,
etc.
In careful, elegant experiments, scientists have also shown that
developmental exposure can heighten sensitivity to carcinogens later in
life. For example, studies of the industrial chemical, ethylene thiourea
(ETU), found that perinatal exposures alone did not affect cancer risk.
Individuals that had been exposed perinatally, however, developed more
cancers when exposed in adulthood than did others, also exposed in
adulthood, who had not been exposed perinatally (Chhabra
et al. 1992).
They conclude this section of their review:
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"Thus, as seen from all the preceeding information, industrial
chemicals, drugs, and radiation have been associated with an
elevated incidence of neoplasms in both experimental animals and in
people following early life stage exposures. These studies also
suggest that fetal susceptibility (lack of metabolism, protective
barriers not formed, etc.), sensitive populations (strain
differences), and critical periods of target organ development are
key elements in the response to environmental carcinogens." |
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Birnbaum and Fenton then turn their focus specifically to
endocrine-disrupting compounds, beginning with a reminder that fetal
exposure to one endocrine disruptor, diethystilbestrol, is clearly
linked to vaginal cancer in young adult women and possibly linked to
testicular cancer in young adult men. Beyond those cases, there
have been almost no human epidemiological studies examining links
between developmental exposures and subsequent cancer risk.
Experimental work with animals is more extensive, however, and as above
with exposures in general, it shows convincingly links between exposures
and cancer causation. The classic case here also is diethylstilbestrol,
but addresses many other compounds also.
For example, when pregnant mice are injected with genistein (a
phytoestrogen abundant in soy), their female daughters develop mammary
gland tumors. Neonatal mice injected with
very low levels of genistein develop uterine cancer. Despite these
results and the popularity of soy formula, according to Birnbaum and
Fenton "there is a dramatic lack of epidemiologic studies
evaluating the effect of maternal (fetal) or infant soy
consumption and correlation with breast, uterine, or testicular cancer."
Polyhalogenated aromatic hydrocarbons
Birnbaum and Fenton provide an excellent short synopsis of experimental
work on the polyhalogenated aromatic hydrocarbons, that family of
brominated and/or chlorinated compounds that include the polychlorinated
biphenyls (PCBs), polybrominated biphenyls (PBBs) and dioxins. Animal
experiments establish definitive causal links between developmental
exposure to an array of these compounds and adverse effects later in
life, including cancers.
Specifically with respect to dioxin, "there have been at least 18
published animal cancer studies in rats, mice, hamsters, and fish
demonstrating cancer positive outcomes in both sexes and at multiple
sites. Experimental studies have also demonstrated that dioxins are
potent tumor promoters, enhancing both the incidence and multiplicity of
tumors at multiple sites following initiation with a direct acting
mutagen."
Birnbaum and Fenton acknowledge that evidence from animal experiments
about dioxin's link to mammary tumors is contradictory, but they point
to
very recent human epidemiological work indicating an association
between developmental exposure and heightened breast cancer risk. In
general, the published animal research on in utero exposure
indicates that dioxin induces changes in mammary gland development and
structure that prolong the developmental period of sensitivity to
carcinogenesis. One interesting set of animal experiments involved
prenatal exposure to dioxin followed by exposure to DMBA at sexual
maturity. This more than doubled the number of mammary tumors. Another
suggests effects on maternal pituitary weight and prolactin levels
consistent with elevated estrogen levels.
Atrazine and Bisphenol A
Recent studies of these two compounds show that in utero exposure can
prolong the period of sensitivity to carcinogens. Atrazine also clearly
alters the pattern of mammary gland development around puberty.
Birnbaum and Fenton's concluding paragraph, below, should be read by all
epidemiologists contemplating work on endocrine disruption and
carcinogenesis, as well as by policy advocates, reporters and editorial
writers. It effectively rebukes any claims (e.g.,
in the New York Times) that existing studies on the links between
EDCs and cancer risk exonerate the contaminants.
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Human Impact?
All of these studies have demonstrated that prenatal exposure to
EDCs can alter the hormonal mileau, reproductive tissue development,
and susceptibility to potential carcinogen exposure in the adult.
These compounds are not genotoxic, yet can have significant adverse
health outcomes. We must ask the questions: Are the appropriate,
sensitive animal strains being utilized to test for
endocrinologically-based diseases, such as breast cancer? Are many
of the adult rodents whose brain and endocrine function are fully
developed relatively insensitive when exposed to EDCs as adults?
There have been epidemiological studies investigating the
association of environmental chemicals, including both
organochlorines, such as PCBs and atrazine, with breast cancer
incidence (Sasco 2001). These particular studies have measured the
levels of exposure of these chemicals in adult women who develop
breast cancer. Could we be trying to correlate exposure and effect
at the wrong time? If it is prenatal, or early life stage, exposure
that is critical to disease susceptibility, why are we measuring
environmental chemicals in people once they have developed breast
cancer? The critical exposure window may have been much earlier. |
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