Fact
Sheets
Immune System
Issue: Interaction
between the immune and endocrine systems is well documented and therefore
it has been suggested that the immune system may be susceptible to endocrine
disruption. The immune system can be affected by the direct actions
of chemicals on specific target components of this system characterized
by immunosuppression, which can lead to decreased resistance to microbial
agents or immunoenhancement, leading to allergy.
Trends: Generally,
mortality from infectious diseases in industrialized countries has decreased
in the last century. This can be attributed to improved sanitation,
housing and nutrition and the introduction of effective immunizations
and therapeutic agents. In the past twenty years, however, a small rise
in the mortality rate from infectious diseases has occurred due to increased
antibiotic resistance and the emergence of AIDS and other viral infections.
The incidence of asthma, an immune disorder, has increased world-wide
at the rate of about 50% per decade. Risk factors for asthma include
exposure to indoor allergens (dust mites, cats, cockroaches), tobacco
smoke, chemical irritants and genetics. It is suspected that the rise
in asthma incidence is related to the increase in urbanization, but
this requires further study. Asthma is associated with inflammation
of the air passages in the lungs resulting in swelling and restriction
of the airways. An underestimated risk factor for asthma is allergic
rhinitis, another hypersensitivity disorder, characterized by allergen-induced
inflammation of the membranes lining the nose.
Consistency of
the data: Evidence regarding a cause-effect relationship between
endocrine-disrupting chemicals and immune system dysfunction is controversial.
Many studies have reported that accidental exposures to environmental
toxicants (PCBs, PCDFs) have been associated with immune dysfunctions
including respiratory ailments and skin lesions in both exposed individuals
and in children exposed in utero. However, in many cases immune parameters
reported for exposed individuals were within the normal range. In another
example of accidental exposure, Vietnam veterans exposed to TCDD (Agent
Orange) have reported health effects as a result of their exposure;
however, immune parameters are not significantly different from unexposed
men. Chronic occupational exposure to low levels of chemicals is not
strongly associated with immune dysfunction. While there are some changes
in the levels of immune system parameters, there is no evidence of increased
incidence of disease. Lactational transfer of endocrine-disrupting chemicals
to children has been shown to be associated with alterations in lymphocytes
and immunoglobulins. There are several studies demonstrating an increased
risk of developing otitis media with pre- and post-natal organochlorine
exposure, while other studies failed to find an association. In general,
epidemiological studies may report increased incidences of a particular
health concern, however, changes in immune parameters (antibodies, lymphocytes)
are often not observed.
Experimental
evidence: It is well-established that environmental toxicants can
affect immune system parameters; however, it is controversial whether
these observed adverse effects are mediated by an endocrine-disrupting
mechanism of action as opposed to direct toxicity. Children and adolescents
exposed to PCBs and PCDFs in Taiwan through consumption of contaminated
rice oil (YuCheng disease) exhibited decreased serum IgA, IgM, cytotoxic
T cells and suppressor T cells with cell-mediated immune system dysfunction.
Infants born to mothers exposed during pregnancy had increased incidence
of respiratory infections and middle ear diseases. In a study of Inuit
children, breast milk levels of organochlorines (p,p'-DDE, hexachlorobenzene,
dieldrin) were correlated with increased incidence of ear disorder otitis
media. Contamination of the arctic food chain by organochlorines has
led to the bioaccumulation of contaminants in human populations inhabiting
the arctic region. Contaminants, particularly lipophilic organochlorines,
are transferred to nursing infants through breast-feeding. The incidence
of non-Hodgkin lymphoma (NHL) has increased in many countries with risk
factors for the disease including exposure to certain pesticides, organochlorines
and Epstein-Barr virus. In a case-control study serum levels of PCBs,
p,p'-DDE, chlordanes, hexachlorobenzene and other contaminants were
measured in individuals with NHL (cases) and controls. Antibody titers
to the Epstein-Barr antigen were correlated to an increased risk for
NHL and were correlated to concentrations of organochlorines. High serum
concentrations of the PCB-type chemicals and the chlordanes were associated
with increased risk for NHL. The effects of environmental toxicants
on the immune system have been widely studied using animal models. TCDD
has been shown to induce premature terminal differentiation of thymocytes
leading to changes in the thymic cortical epithelium resulting in atrophy
of the thymus in rodents. TCDD suppresses cell-mediated immunity, delayed
hypersensitivity and generation of cytotoxic T cells in a dose-dependent
manner. In wildlife studies, birds exposed to organochlorines exhibit
immunosuppression. However, the mechanisms for these effects are not
known.
Biological plausibility:
Many potential endocrine toxicants have been shown to be immunotoxic;
however, it is controversial whether the effects on the immune system
are mediated through disruption of the endocrine system or are the result
of direct toxicity. In animal models and cell lines, chemicals such
as TCDD, some PCBs, PCDD, PCDFs have been shown to bind to the aryl
hydrocarbon receptor (AhR). Thus, by binding to the receptor, these
organochlorine chemicals trigger AhR-mediated expression of genes involved
in cell proliferation and differentiation causing myelosuppression,
immunosuppression, thymic atrophy and inhibition of immune complement
system components in many animal species. Timing of exposure is relevant
as impairment to the immune system is more severe if exposure occurs
during pre- or post-natal life compared to exposure in adult animals.
Maturation of the immune system in rodents is especially vulnerable
to adverse effects of dioxin-like compounds, chlordane, hexachlorobenzene,
polycyclic aromatic hydrocarbons, DDT, and kepone. Similarly in humans,
the immune system is vulnerable to chemical exposure during fetal and
post-natal development.
Reproductive hormones
have been shown to regulate the immune system. Pre-menopausal women
tend to have higher immunoglobulin concentrations, stronger primary
and secondary responses and increased resistance to the induction of
immunological tolerance. The predominance of autoimmune diseases (Graves'
disease, systemic lupus erythematosis, multiple sclerosis, rheumatoid
arthritis) among women suggests that reproductive steroid hormones may
modulate immunologic susceptibility. Estrogen has been shown to regulate
the expression, distribution and activity of immune chemicals called
cytokines. Studies using mouse lymphocytes have shown that estrogen
enhances production of immune chemicals such as interleukins and interferons
while androgens decreased the production of these chemicals. The immune
system, through cytokine and interleukin-mediated pathways can regulate
the reproductive system by inducing the release of gonadotropins LH
and FSH.
Conclusions:
There is insufficient evidence to demonstrate that exposure to toxicant-induced
disruption of the immune system involves an endocrine mechanism. Many
studies report increased incidence of adverse health effects following
exposure, however, immune parameters, where measured, are often within
the normal range. Animal studies provide some evidence that endocrine
toxicants may impair the immune system, but additional studies are required.
The regulation of the immune system by the endocrine system may render
the immune system vulnerable to endocrine disruption. A greater understanding
of both systems, along with sound epidemiological data are required
to determine whether chemicals alter immune function via an endocrine
disruption mechanism of action.