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The Complexity of the Body
This page gives a very brief introduction
to the endocrine, immune and nervous systems, and the important
role of development.
This page focuses mainly on interactions
between the endocrine system and the immune and nervous systems,
including some recent references. If you want to know more I
would recommend looking at recent text books covering each of
the three systems and development. Knowledge of these systems
is advancing rapidly, so the newer the text book, the better.
The hormonal or endocrine system
This system is the main subject of this
web site, particularly the reproductive hormones. Hormones generally
carry fairly long-lasting messages, in contrast to the rapid
signalling of the nervous system. In 1997 more complexity was
added to the attempts to understand the endocrine system, and
potential effects of chemicals on it, when it was discovered
that the 'female' hormone oestradiol is essential for male
fertility (Sharpe, 1997). If this wasn't enough, it is now clear
that there is not just one oestradiol receptor; there are several,
and they all behave slightly differently, with differing levels
in different tissues (Petersen et al., 1998).
The immune system
The immune system is responsible for resisting
infectious agents, environmental substances and foreign or damaged
cells (Dean and Murray, 1991). The capacity for immune response
is determined early in development, so damage early in life will
persist (Colborn, 1996). The immune and endocrine systems are
linked by a variety of signalling systems, and much research
on wild animals has demonstrated that endocrine disrupting chemicals
can reduce the effectiveness of the immune system (Kavlock et
al., 1996). A lot of this research has focused on marine animals
and birds; for example, high levels of PCBs and DDT in the blood
of dolphins was associated with decreased immune function and
increased incidence of infection (Kavlock et al., 1996).
The nervous system
The function of the nervous system is the
rapid communication of signals between different parts of the
body, and the processing of these signals. The most complex part
of the nervous system is the brain, where most of the processing
occurs. Although most of the nervous system is protected from
potential toxicants by the blood-brain barrier, some chemicals
can penetrate this barrier (Anthony and Graham, 1991). In addition,
this barrier is not fully developed until after birth, which
is why the developing foetus is so sensitive to chemicals such
as alcohol.
A US EPA workshop concluded that a variety
of endocrine disrupting chemicals, including some PCBs, dioxins,
DDT and chlorinated pesticides, are capably of producing neurotoxicity
(Kavlock et al., 1996). Effects reported in the literature included
changes in behaviour, learning and memory attention. 'Our Stolen
Future' (Colborn et al., 1996) describes several of these studies.
Most of these toxic effects are believed to occur due to the
endocrine disrupting chemicals influencing the development of
the nervous system.
The rest of the body
Other parts of the body are also affected
by hormones. For example, blood vessels are influenced by oestrogen
levels, with oestrogen exposure leading to relaxation of the
walls of the vessels. Ruehlmann et al (1998) have found that
4-octyl phenol, p-nonylphenol and o,p'-DDT have the same effect
as oestrogen.
Develoment
The timing of administration of a hormone
disrupting chemical is particularly important for foetuses and
young children, as the body's systems are most sensitive when
they are under construction (Manson and Wise, 1991). During this
period different events are occurring on different days, so providing
small windows of time when the developing organism is extremely
sensitive to hormone disrupting chemicals, for example during
the formation of the testes (see the health
page). Diethylstilbestrol (DES), a synthetic oestrogen, was
taken by more than 5 million pregnant women between the late
1840s and the early 1970s, and led to many reproductive abnormalities
in both male and female offspring (Toppari et al., 1996). Experiments
on rats have since demonstrated how DES exposure at particular
stages of foetal development leads to reproductive system damage,
similar to that exhibited by the human victims (Toppari et al.,
1996).
It is known that the developing foetus
is the most sensitive stage in human development of organs such
as the testes). The effects of many of these chemicals are additive;
there is more debate about the extent of more than additive effects
(see issues page), so exposure to a
range of chemicals at a low levels has the same effect as exposure
to one chemical at a higher level.
Crucial windows of sensitivity in male
development
The development of the testis occurs almost
entirely during early development in the womb. It is in this
period that the Sertoli cells differentiate, and any exposure
to oestrogen at this time reduces the number of Sertoli cells
produced (Jensen et al., 1995). The Sertoli cells are responsible
for producing sperm in later life, and it has been shown that
the number of Sertoli cells is directly related to the sperm
count, so fewer cells will lead to a lower sperm count (Jensen
et al., 1995). It is also believed that abnormal germ cells,
formed in early development, are responsible for most testicular
cancers in later life (Jensen et al., 1995).
The oestrogen diethylstilbestrol (DES)
was given to > 5 million pregnant mothers in the period between
the late 1940s and the early 1970s to prevent miscarriage. Its
use was stopped after a high incidence of a rare cervical cancer
in pubertal girls exposed to DES in the uterus. It was later
found that male offspring also had a higher level of reproductive
abnormalities, including low sperm counts (Jensen et al., 1995).
The case of DES is a clear indication that exposure of the foetus
to external oestrogens can result in reproductive problems later
in life (Toppari et al, 1996).
For the adult males, direct toxic effects
on sperm production by chemicals such as phthalates
could also be an issue. However as far as oestrogenic effects
go, it is clear that the final 3 months of pregnancy and the
first few months of life will be where any exposure of a male
to oestrogens is likely to have the greatest effect. The research
showing that metabolites of DDT can block
the male hormonal system is worrying.
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This page was last
updated in October 1999
Return
to the hormone disrupting chemicals home page
References
Jensen, T.K., Toppari, J., Keiding, N.,
Skakkebaek, N.E. 1995. Do environmental estrogens contribute to
the decline in male reproductive health?. Clinical Chemistry 41:
1896-1901.
Toppari, J., Larsen, J. C., Christiansen,
P., Giwercman, A., Grandjean, P., Guillette, L. J., Jégou,
B., Jensen, T. K., Jouannet, P., Keiding, N., Leffers, H., McLachlan,
J. A., Meyer, O., Müller, J., Rajpert-De Meyts, E., Scheike,
T., Sharpe, R., Sumpter, J. and Skakkebaek, N. E. 1996. Male reproductive
health and environmental xenoestrogens. Environ. Health Persp.
104 Suppl. 4: 741-803.
Anthony, D. C. and Graham, D. G. 1991. Toxic
responses of the nervous system. In: Casarett and Doull's Toxicology:
The Basic Science of Poisons. pp. 407-429. Amdur, M. O., Doull,
J. and Klaassen, C. D. Eds., Pergamon Press, New York.
Colborn, T. 1996. Statement from the work
session on the chemically-induced alterations in the developing
immune system: The wildlife/human connection. Environ. Health
Persp. 104 Suppl. 4: 807-808.
Colborn, T., Dumanoski, D. and Myers, J.
P. 1996. Our Stolen Future. Penguin, New York.
Dean, J. H. and Murray, M. J. 1991. Toxic
responses of the immune system. In: Casarett and Doull's Toxicology:
The Basic Science of Poisons. pp. 282-333. Amdur, M. O., Doull,
J. and Klaassen, C. D. Eds., Pergamon Press, New York.
Kavlock, R. J., Daston, G. P., DeRosa, C.,
Fenner-Crisp, P., Gray, L. E., Kaattari, S., Lucier, G., Luster,
M., Mac, M. J., Maczka, C., Miller, R., Moore, J., Rolland, R.,
Scott, G., Sheehan, D. M., Sinks, T. and Tilson, H. A. 1996. Research
needs for the risk assessment of health and environmental effects
of endocrine disruptors: A report of the U.S. EPA-sponsored workshop.
Environ. Health Persp. 104 Suppl. 4: 714-740.
Petersen, D. N., Tkalcevic, G. T., Koza-Taylor,
P. H., Turi, T. G. and Brown, T. A. 1998. Identification of estrogen
receptor b2, a functional variant of estrogen receptor b expressed
in normal rat tissues. Endocrinology 139: 1082-1092.
Ruehlmann, D. O., Steinert, J. R., Valverde,
M. A., Jacob, R. and Mann, G. E. 1998. Environmental estrogenic
pollutants induce acute vascular relaxation by inhibiting L-type
CA2+ channels in smooth muscle cells. FASEB Journal 12: 613-619.
Sharpe, R. M. 1997. Do males rely on female
hormones? Nature 390: 447-448.
Arnold, S. F., Robinson, M. K., Notides,
A. C., Guillette Jr, L. J. and McLachlan, J. A. 1996. A yeast
estrogen screen for examining the relative exposure of cells to
natural and xenoestrogens. Environ. Health Persp. 104: 544-548.
Jobling, S., Reynolds, T., White, R., Parker,
M. G. and Sumpter, J. P. 1995. A variety of environmentally persistent
chemicals, including some phthalate plasticizers, are weakly estrogenic.
Environ. Health Persp. 103: 582-587.
Kavlock, R. J., Daston, G. P., DeRosa, C.,
Fenner-Crisp, P., Gray, L. E., Kaattari, S., Lucier, G., Luster,
M., Mac, M. J., Maczka, C., Miller, R., Moore, J., Rolland, R.,
Scott, G., Sheehan, D. M., Sinks, T. and Tilson, H. A. 1996. Research
needs for the risk assessment of health and environmental effects
of endocrine disruptors: A report of the U.S. EPA-sponsored workshop.
Environ. Health Persp. 104 Suppl. 4: 714-740.
McLachlan, J. A. 1997. Synergistic effects
of environmental estrogens: Report withdrawn. Science 277: 462-463.
Manson, J. M. and Wise, D. L. 1991. Teratogens.
In: Casarett and Doull's Toxicology: The Basic Science of Poisons.
pp. 226-254. Amdur, M. O., Doull, J. and Klaassen, C. D. Eds.,
Pergamon Press, New York.
Soto, A. M., Sonnenschein, C., Chung, K.
L., Fernandez, M. F., Olea, N. and Serrano, F. O. 1995. The E-SCREEN
assay as a tool to identify estrogens: An update on estrogenic
environmental pollutants. Environ. Health Persp. 103: 113-122.
Toppari, J., Larsen, J. C., Christiansen,
P., Giwercman, A., Grandjean, P., Guillette, L. J., Jégou,
B., Jensen, T. K., Jouannet, P., Keiding, N., Leffers, H., McLachlan,
J. A., Meyer, O., Müller, J., Rajpert-De Meyts, E., Scheike,
T., Sharpe, R., Sumpter, J. and Skakkebaek, N. E. 1996. Male reproductive
health and environmental xenoestrogens. Environ. Health Persp.
104 Suppl. 4: 741-803.
URL: http://website.lineone.net/~mwarhurst/complexity.html