Carcinogenic Exposures
The third area where research remains inconclusive concerns the
range of agents that contribute to cancer risk among children. For
a substance to cause cancer that appears in childhood it must operate
with a relatively short latency period. Because children don't have
the same opportunity to develop the lifestyle choices that increase
risk of cancer in adults, we can say with greater certainty that
most childhood cancer is likely explained by involuntary exposure
to environmental agents, narrowly defined. There are relatively
few well-established environmental exposures clearly associated
with pediatric cancers.
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"The lifestyle of toddlers
has not changed much over the past half century. Young children
do not smoke, drink alcohol, or hold stressful jobs. Children
do, however, receive a greater dose of whatever chemicals
are in air, food, and water because, pound for pound, they
breathe, eat, and drink more than adults do. . . They are
also affected by parental exposures before conception, as
well as by exposures in the womb. "29
(Sandra Steingraber, PhD)
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All of us are likely exposed to countless carcinogens throughout
our lives. Some of these are naturally occurring substances or agents,
such as solar radiation, radon or carcinogens found in foods, such
as aflatoxins, the toxic mould often found in peanuts, peanut butter,
corn and cheese.30 Others are natural substances
that become carcinogenic to humans through activities such as extraction,
refining and use in the manufacture of various products.
Asbestos, arsenic, uranium, silica and nickel are all examples
of such carcinogens.31 The category of
carcinogens, however, that has evoked considerable attention, especially
for their ability to cause cancer in childhood, includes synthetic
chemicals used in plastics, pesticides, dyes and pharmaceuticals,
representing many hundreds of different agents or substances.
It is beyond the scope of this document to adequately outline how
carcinogenicity is determined and what substances are deemed to
be carcinogenic to humans. It is useful, however, to understand
that environmental hazards or agents are generally classified, according
to the strength of the scientific evidence and according to scientific
opinion, into one of four categories:32
| Group 1. Sufficient evidence of carcinogenicity |
Group 2a. Probable carcinogens
Group 2b. Possible carcinogens |
| Group 3. Not classifiable as to carcinogenic
risk to humans (due to inadequate evidence) |
| Group 4. Probably not carcinogenic
to humans |
Of the many thousands of chemicals in current use, there are relatively
few where there is sufficient toxicological information to definitively
characterize cancer-causing ability (i.e., Group 1 carcinogens)
in humans. In the context of childhood cancers, the data gaps are
considerable. Although a number of etiological agents have been
proposed as causal for different types of childhood cancer, very
few have been confirmed.
The environmental carcinogens that are known to cause childhood
cancers include some medications such as diethylstilbestrol and
chemotherapeutic drugs, radiation and certain industrial and agricultural
chemicals.34 Here we discuss in further
detail only the environmental exposures linked to cancer in the
young.
Radiation
Several forms of high frequency radiation (including ultraviolet,
roentgen and gamma rays) are well-established human carcinogens.
Radiation induces cancer primarily via damage to DNA, but there
is some evidence that immunosuppression may be the mechanism involved
in some cancers.35 There is some evidence
that children are more susceptible to the effects from radiation
than are adults.36
Evidence from high dose exposure circumstances (e.g., radiotherapy
for other cancers, atomic bomb survivors) clearly indicates the
link to a number of different cancers in children. Ten years after
the Chernobyl accident, for example, there are published reports
of increased frequency of thyroid cancer in children living or born
in the areas with highest exposure to radioactive contamination.37
Leukemia is another childhood cancer associated with postnatal exposure
to ionizing radiation. There is increased risk of developing additional
secondary cancers after radiotherapy treatment for Hodgkin's disease.38
The effects of exposure to lower dose radiation are less
clear and somewhat more controversial.39
Several case-control studies indicate that prenatal exposure to
X-rays is linked with moderate increases in leukemia in children. For example, a study of twins demonstrated double the risk of leukemia
in those irradiated prenatally compared to those who were not irradiated.40
Paradoxically, cohort studies following children exposed to radiation
from nuclear weapons testing have not shown the expected increase
in childhood leukemia.41 Radon, a naturally
occurring radioactive decay product of radium that can be found
in air and groundwater, is linked to lung cancer in adults. One
study has reported a dose-related association between radon levels
in drinking water and elevated leukemia in children; however, there
is clearly need for further study of this relationship.42
Several studies have attempted to explore the possibility that
parental, specifically paternal, preconceptional exposure
to ionizing radiation carries a greater risk of offspring developing
leukemia in childhood, but the interpretation of results has been
problematic.43 Many of these studies have
had only small numbers of cases to examine, and because study fathers
were frequently highly exposed throughout their child's life, it
was difficult to pinpoint the exact timing of the relevant exposure.44
Electromagnetic Fields (EMFs)
Electric and magnetic fields, or EMFs, are low frequency currents
associated with electricity. People are exposed to EMFs from multiple
sources, including electrical transmission and distribution lines
and a variety of electrical appliances found in homes, schools and
the workplace. There has been great public concern and controversy
surrounding the hypothesis of associations between EMF exposure
and brain cancer and leukemia in children. The suggestion that EMFs
were linked with excess risk of cancer came initially from studies
of occupationally exposed adults in whom there were modest increases
in some rare cancers. The potential for this association to be causal
has been vigourously debated in scientific circles.
Since the first study reporting an association between childhood
cancer and EMF exposure, several other researchers have attempted
to duplicate these results; however, there has been little consistency.
A 1997 review and meta-analysis by the National Research Council
of eleven such epidemiological studies proposed that while there
is some evidence for a positive association between exposure to
high magnetic fields and childhood leukemia, data are inadequate
to reach a firm conclusion.45
Analysis of studies since the NRC review has not significantly
changed the conclusions; however, Loomis and colleagues stress that
no study has shown definitively that magnetic fields are not
carcinogenic.46 As a result, some sources
suggest that people adopt prudent avoidance of excess exposure to
EMFs, particularly with respect to children.47
Organic Solvents
Organic solvents are major industrial chemicals that, because of
their presence in many products used in homes, schools and workplaces,
are potentially abundant in the environment. They are also known
as volatile organic compounds (VOCs) because of their tendency to
evaporate at room temperature. As a result, breathing in air that
is contaminated with organic solvents is how people are most often
exposed.48
The vast majority of epidemiological studies that assess carcinogenicity
concern solvents as a group, with few identifying specific
solvents that increase cancer risk. There is fairly consistent evidence
that occupational exposure to solvents in parents (the father in
particular) is associated with increased risk of brain and urinary
tract cancers and leukemia in their children.49
Children may be exposed to these chemicals when they are
transferred home on parent's clothing or skin, or via exhaled breath
or breast milk.50
Benzene is one organic solvent that has been specifically
linked to higher rates of leukemia in the offspring of exposed parents.
There are strongest associations for fathers exposed to gasoline,
which is the prime source of environmental benzene.51
Benzene is a known carcinogen in adults and has been shown to cause
chromosomal abnormalities and changes in blood-forming cells in
the liver and spleen of fetal mice, which lends biological plausibility
to the association with childhood leukemia.52
The consistent associations between childhood leukemia and paternal
occupation as painters, printers or in motor vehicle related work
(e.g., gas station attendants, mechanics, drivers, etc), may be
explained by exposure to solvents, although there are other chemicals
that might also be involved. For example, people exposed to gasoline
and gas exhaust are also exposed to carcinogens such as dichloroethane,
dibromomethane and benzo[a]pyrene.53
Other studies are lending weight to the hypothesis that childhood
brain cancer is associated with parental solvent exposure, particularly
where a father's occupation involves exposure to gasoline, trichloroethylene,
methylethylketone or freon.54
The majority of studies summarized in a recent review by Colt and
Blair suggest that it is preconceptional and prenatal exposures
to organic solvents that carry the greatest relative risks for childhood
cancer although some studies have also noted an increased risk with
postnatal exposure as well.55 These authors
identify that more attention must be paid to adequately assessing
the relevant exposure time frame as well as focusing on the influence
of maternal exposures to organic solvents.
Pesticides
Experimental studies and in vitro tests have suggested that
there are carcinogens represented from all major classes of pesticides
including organochlorine and organophosphate insecticides, herbicides,
fungicides and fumigants.56 The International
Agency for Research on Cancer (IARC) has identified over 45 pesticides
as being potential or known carcinogens in animals. Almost half
of these are still registered and in common use in the US, including
the herbicide atrazine; the insecticides dichlorvos, dicofol and
lindane; and the fungicides captan, pentachlorophenol and creosote.57
Epidemiological evidence of pesticides as a risk factor in childhood
cancer is variable. Some studies suggest that certain childhood
cancers may be related to pesticide exposures either directly or
via parental exposure. A large Swedish population-based cohort study
indicates increased risk of nervous system tumours, but not leukemia
in children whose fathers were exposed to pesticides.58
Additional Swedish research did demonstrate an association between
non-Hodgkin's lymphoma (NHL) and exposure to phenoxy herbicides
in a case-control study.59 A large retrospective
cohort study of Norwegian farm families has determined that there
was increased risk of developing certain brain tumours, non-Hodgkins
lymphoma, Wilms tumour and other cancers of infancy in farm children,
associated with various proxy measures of parental pesticide exposure
and use.
Daniels and co-workers conducted a meta-analysis of 31 studies
that examined the association between pesticide exposure and incidence
of various childhood cancers.61 Despite
inadequacies in exposure assessment, these researchers conclude
that there is indeed reason to suspect that pre-conceptional, prenatal
and early childhood exposures to pesticides are associated with
moderate increases in childhood brain tumours and leukemias. Home
use of pesticides appeared to account for the greatest risk of these
cancers.62 For example, brain cancer was
found to be in association with childhood use of lindane for lice
treatment.63 Others have suggested that
using no-pest strips in the home also increases the risk of childhood
brain tumours64 and leukemias.65
Tobacco
There is incontrovertible evidence for the association between
ETS and cancer in adults from both toxicological and epidemiological
studies. Surprisingly, investigation of the association between
pre- and postnatal passive smoking and the incidence of childhood
cancer has not yielded similarly definitive findings.
A recent review of roughly 50 relevant epidemiological studies
stated that there were only slightly increased relative risks for
childhood brain tumours and leukemia-lymphoma with pre- and postnatal
passive exposure to ETS.66 These findings,
however, are bolstered by toxicological and metabolic data demonstrating
damage to DNA in the fetus as well as genotoxic effects in spermatozoa,
suggesting that the risk of cancer in childhood from passive exposure
to ETS early in life cannot be ignored.67
Infectious Agents
Some propose that polyoma viruses passed on to the fetus transplacentally
might explain higher risk for childhood brain cancer, since these
viruses can cause DNA mutations. A number of researchers suggest
that clusters of childhood leukemia could represent the outcome
of unusual epidemics of infectious disease spread by population
mixing.68
A similar theory suggests that childhood leukemia occurs when a
child with a vulnerable, unchallenged immune system has proliferation
of white blood cells from DNA damage caused by a culprit infectious
organism. These hypotheses remain speculative despite accumulation
of epidemiological research as "no viruses or definitive immunological
mechanisms have been identified."69
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