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African Journal of Biomedical Research
Ibadan Biomedical Communications Group
ISSN: 1119-5096
Vol. 6, Num. 3, 2003, pp. 113-118
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African Journal of Biomedical Research, Vol. 6, No. 3, Sept, 2003,
pp. 113-118
Mini-Review Article
MOLECULAR EPIDEMIOLOGY: A BETTER APPROACH FOR THE
EARLY DETECTION OF PATHOPHYSIOLOGIC RESPONSE TO ENVIRONMENTAL TOXICANTS
AND DISEASE
ANETOR J.I. 1* , ADENIYI F.A.A. 1 , OLALEYE
S.B.2
Departments of 1Chemical Pathology and Physiology2 ,
College of Medicine , University of Ibadan . Ibadan , Nigeria .
Received: June 2003
Accepted: September
2003
Code Number: md03050
Our environment is becoming increasingly contaminated by a profusion of
substances in the form of industrial and Municipal Waste, air and water pollutants;
by heavy metals (such as lead) herbicides, pesticides, cosmetics and so on.
The number of chemicals that affect man increases at alarming rates. These
agents may be dangerous because they produce biochemical, genetic, structural
or physiological lesions in a significant segment of the population. The
importance of elucidating the nature and the mechanisms of physiological
and toxicological reactions has been emphasized in the investigations of
occupational and environmental diseases, such investigations have revealed
that the clinical manifestations of intoxication may have their origin in
injurious effects of subcellular or biochemical types. Slight to moderate
derangements in metabolism may impair the functional activity of organs and
lead to subclinical or overt clinical effects. These may elude detection
or recognition of their health implications unless biomarkers, the functional
components of molecular epidemiology are employed. Molecular epidemiology
is an approach which aims to examine aetiology of disease in a more precise
way by focusing on biomarkers of disease risk rather than relying on the
actual occurrence of disease. Such studies can be carried out in a short
time and with relatively small numbers of subjects compared with conventional
epidemiology, which though currently more popular merely reveals association,
and causal links often remain obscure. Detection of early biochemical lesions
that are related to subsequent changes in structure and physiology would
be useful as early indicators of environmental hazards that produce disease
in humans, that is by employing molecular epidemiology. This will be greatly
enhanced by newer tools, such as toxicogenomics and metabonomics.
Key
words: Molecular epidemiology, Environmental toxicant,
Pollutants, Lead, Pathophysiologic response, , Toxicogenomics.
INTRODUCTION
As societies throughout the world are increasingly moving to greater levels
of urbanization and industrial development, public concern is mounting over
the state of the environment and much attention is now being paid to improving
the environment for future generations. Probably the most disturbing aspect
of the attendant pollution to urbanization and industrial development is the
increasing presence of toxic chemicals in the natural environment. The large
scale production and application of synthetic chemicals and their subsequent
pollution of the environment is now a problem of serious concern in most industrialized
countries and must be viewed as an extreme threat to the self-regulating capacity
of the biosphere in which we all live.
The environment in the developing World including Nigeria as a result of progressive
industrialization, which entails the increasing use of various chemicals, is
also becoming increasingly contaminated by a profusion of substances in the
form of industrial and municipal waste, air, water pollution by heavy metals,
herbicides, pesticides, cosmetics food additives etc.
The number of chemicals that affects man increases at an alarming rate (Brodie,
1970). These agents may be dangerous because they produce biochemical or physiological
lesions in a significant segment of the population.
The importance of elucidating the nature and the mechanisms of physiological
and toxicological reactions has been emphasized in the investigations of occupational
and environmental disease (De Bruin, 1971), such investigations have revealed
that the clinical manifestations of intoxication may have their origin in injurious
effects of subcellular biochemical types. Slight to moderate derangement in
metabolism may impair the functional activity of organs and lead to subclinical
or distinct clinical effects. These may elude detection or recognition of their
implications unless biomarkers, the functional constituents of molecular epidemiology
are employed. Too often in the past such hazards have been defined only after
outbrakes of human cases have occurred usually by techniques of conventional
epidemiology.
The detection of early biochemical lesions that are related to subsequent
changes in structure and physiology would be useful as early biomarkers of
environmental hazards that produce disease in humans perhaps even more important
in the long term is basic understanding of mechanisms by which environmental
chemicals produce their effects which appear as the only rational basis for
predicting the hazards associated with the mixture of chemicals currently in
use globally.
Lead Toxicity: A Prime Example of Environmental Pollution
Since the age of metals began when man first learnt to extract them
from ores and work them, exposures to industrial lead have vastly increased.
Man was exposed to lead in Asia Minor 4500 years ago as a by product of silver
smelting (Schroeder, 1973) owing to its being an insidious and slow acting
toxin, the use of lead by man continued for 4300 years without suspecting toxicity.
Only since about two and a half centuries has he become aware of some of the
extreme toxic effects of lead and learned to avoid them. In the past eight
years more and more of these effects have been reported. Low level lead exposure
that was previously thought innocuous is now also of great concern (Needleman
and Allred, 1990).
The highest known exposures of human beings to lead before the age of petrol
probably occurred in ancient Rome . Here amphorae stored syrups and wine, lead
pipe carried water to the houses of the rich Romans, Soft water dissolves lead,
lead cosmetics were used by the ladies. There is little doubt that lead poisoning
was endemic among those who could afford such luxury. Infact (Gilfillan, 1965)
believes that lead poisoning resulting in still births, spontaneous abortion
(lead has been used as an abortificent) and sterility was responsible for the
low birth rate of the upper classes of the Roman empire which led to the ultimate
fall of the Roman Empire. It is not also known if the global environmental
pollution accounts for the decrease in fertility and drop in sperm count that
are currently being observed (Carlsen et al, 1992). The male reproductive system
is known to be highly sensitive to some physical and chemical environmental
exposures (Severer and Hassel, 1985). Simple biomarkers like urinary creatine
may serve as early warning sign (Anetor et al, 2000).
There was little lead found in the bones of third century monks, but large
amounts have been reported in those of the eleventh to the nineteenth century.
This may even be greater in our own generation. Nigeria has one of the World's
highest lead content in petrol )Thomas et al, 1999).
Africa 's contribution to lead ( Nigeria is one of the topmost rapidly developing
and restructuring countries in Africa ) to global lead pollution has increased
from 5% in 1980 to 20% in 1996 (Nriagu et al, 1996). Additionally the blood
lead level BLL in the children of many African countries have been reported
to be excessive in some cities. Ninety per cent (90%) of children in Africa
carry BLL above the current safe threshold (Nriagu, 1966).
Many reports have consistently indicated that our own environment (Nigerian)
(Nriagu, 1996) is highly polluted. The increasing environmental pollution given
by high BLL in the general population (Okoye, 1994, Adeniyi and Anetor, 1999,
Anetor and Adeniyi, 2001) is largely attributable to the high lead content
of our gasoline.
Biomarkers in Environmental Toxicology
In order to assess the health risks of exposure to potentially toxic chemicals
biomarkers are essential. The use of and development of biomarkers has recently
become of understandably major interest (Timbrel et al, 1994). With developments
in analytical chemistry and biochemistry, methods have become available to
trace the fate of environmental chemicals in the human body so as to assess
the chemical exposure status of an individual and the risk of disease development
by biomarker determination. Biomarkers can be used for preventive purposes
and for risk assessment. Some sensitive techniques have been developed to detect
DNA damage in human or animal cells. These are being used to assess the impact
of pollutant exposure or genotoxic changes in both the general population and
industrial workers in some countries in Europe and Latin America (Restrepo
et al, 2000). The early detection of occupational diseases is of prime importance
as initial changes are often reversible.
Molecular Epidemiology in Environmental Pollution
Classical epidemiology is the scientific study of disease distribution and
determinants. Epidemiology, however, merely reveals associations and causal
links often remain obscure. Molecular epidemiology appears superior to traditional
epidemiology in the early detection of early biochemical lesions that lead
to subsequent changes in structure and physiology. Molecular epidemiology may
be considered to be the epidemiological correlate of molecular toxicology which
rationalizes on molecular basis the toxicological responses of the organism
to environmental, industrial and domestic chemicals thus providing a firm basis
for evaluation of risk to man. Molecular epidemiology is an approach which
aims to examine aetiology of disease in a more precise way by focusing on biomarkers
of disease risk, rather than relying on the actual occurrence of disease. Such
studies can be carried out in a short time and with relatively small numbers
of subjects compared with conventional epidemiology, which though popular however,
merely reveals association and causal links often remain uncertain. Table 1
shows some of the benefits of Molecular Epidemiology.
Molecular Epidemiology, Toxico-genomics and Metabonomics
Toxicology is the science of the adverse effects of chemicals, drugs,
environmental agents and stressors. Genomics, defines the structure, sequence
(code) and function of the entire DNA complement of organisms. The interface
of these diverse disciplines is called toxicogenomics and is based upon the
application of genomics technologies to define globally the changes in gene
expression (both RNA and proteins as a consequence of exposure to environmental
toxicants (Tennant and Selkirk, 2002). DNA microarray technology enables the
simultaneous measurement of transcription of thousands of genes using micro-chips
containing thousands of probes of complementary DNA (cDNA) immobilized in a
predetermined array. The ultimate application of this technology to environmental
toxicology or indeed general toxicology holds great promise for molecular epidemiology,
though currently faces several formidable problems that need to be surmounted.
Microarray assay approaches have been proposed to investigate the mechanism
of action of endocrine disruptors and as a potential screening method for synthetic
and natural endocrine disruptors (Tennant and Selkirk, 2002). The situation
of endocrine disruptors in Nigeria is currently unknown although this is predicted
to be very high (Anetor, 2002). This is a current concern of the scientific
community, especially SCOPE (Scientific Committee on Problem of the Environment)
and IUPAC (International Union of Pure and Applied Chemistry). Molecular epidemiology
will play a great role in this respect in investigating this problem in this
environment.
The problem of identifying environmental factors involved in the induction
and evolution of human disease, and in conducting safety and risk assessments
of drugs and chemicals, have long been formidable issues. Three major component
for predicting potential human health risk are firstly, the diverse structure
and properties of a huge number (thousands) of chemicals and other environmental
stressors; Secondly, the time and dose parameters that underlie the relationship
between exposure and disease and thirdly, genetic diversity of surrogates to
assess adverse chemical effects. The techniques evolving from the successful
genomics efforts are providing new tools with which to address these intractable
problems of environmental health and toxicology.
The simultaneous analysis of expression of thousands of genes as end points
using cDNA chips or microarrays should allow toxicologists a new comprehension
of toxicological issues. Toxicogenomics, the combined field of toxicology and
genomics thus has become a focus for the research community and regulatory
authorities as a new approach to understanding of the Mechanisms invoived.
It can provide us with very useful data relevant.to difficult areas such as
dose-response relationships, species-to-species extrapolations and exposure
assessment that can not be resolved by traditional toxicological techniques
(Shirai and Asamoto, 2002). Application, of toxicogenomics technology to environmental
toxicology issues can be expected to overcome the limitations of conventional
methods. A great possibility is that toxicogenomics will facilitate differentiation
of gene responses specific to organ system activity from those associated with
non-specific general response. It can be envisaged that efforts with specific
organs like the mammary glands, endometrium, prostate gland and the thyroid
depending upon hormonal activities would be rewarding. Confidence in results
might be raised by combining toxicogenomics thus molecular epidemiology with
traditional toxicological and toxicolpathological findings. Though current
efforts are focused on Endocrine disruption especially the reproductive pathway
(Damstra et al, 2002), it holds great promise for toxicology especially environmental
toxicology.
Closely rated to toxicogenomics is the application of products and by-products
of metabolism. Metabolites are the products of the many intricate biosynthesis
and catabolism pathways that exist in human and other living systems. Historically,
measurement of metabolites in human biofluids has been employed for the diagnosis
of a number of inherited disorders and for assessing exposure to certain xenobiotics.
Traditional analysis approaches have focused on one or a few metabolites.
In recent times, advances in analytical separation and detection methods,
coupled with developments in bioinformatics, have made it possible to measure
and interprete complextime-related metabolite profiles that are present in
biological fluids. The terms metabonomics and metabolomics have been coined
to describe metabolic profiling, although the precise nomenclature including
potential differences between these terms, is still evolving. The application
of metabonomics to study potential environmental contributions to disease was
recently examined at the Division of Extramural Research and Training Science
Planning retreat held 27-28 November 2001 in South Pines, North Carolina (Lawler,
2002). The session highlighted the opportunities and challenges provided by
metabolic profiling which will be used as guidelines of future attempts by
the National Institute of Environmental Health Sciences (NIEHS) to promote
and support the application of molecular and related principles to environmental
health sciences and their full integration to future genomic and proteomic
initiatives. Metabonomics provides an integrated detector of both primary and
secondary disturbances that point to a pathophysiologic process, genetic modification
or xenobiotic exposure.
Abundant opportunities exist for the application of metabonomics to the field
of environmental health sciences or toxicology particularly in the area of
biomarkers of exposure and disease.
Cancer and Environmental Toxicity
Although cancer is perhaps the most feared and best known of the chronic pathologic
effects of environmental chemicals, it should be recognized that environmental
agents may cause other forms of chronic illness including birth defects, reproductive
impairments on behavioural abnormalities.
Environmental factors have however, been estimated to cause more than 85%
of human cancers, but in such cases the term environmental is all inclusive
and refers essentially to all causative agents other than genetic factors (Holbrook,
1990). Environmental factors may infact be responsible for 25% of human cancer,
but such environmental chemicals include those manufactured, those resulting
from the industrial or work environment, natural plant or fungus produced toxins
e.g. aflatoxin and inorganic salts either metallic or nitrate/nitrite.
Table I
Some Specific Derivable Benefits
from Molecular Epidemiology |
- Serve as chemical and biochemical
indicators of toxic exposure
- Biomarkers of damage to DNA
- Signs of early organ dysfunction
- Indicators of inherited hyper susceptibility
- Detection of individual sensitivity to chemicals
- Analytical and diagnostic validity
- Applications in biological monitoring and risk assessment
- Implications for preventive strategies
- Species-to-species extrapolation
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In the case of cancer, measures of DNA damage and mutation are
appropriate biomarkers. These are recognized as early events in the process
of carcinogenesis. It is indeed possible that the current explosion of cases
of cancer in the developed countries which is gradually creeping into the developing
countries is probably due to dearth of methods of molecular epidemiology to
pick the process of carcinogenesis at the initiation stage before it progresses
to the phase of promotion.
The Metabolic Fate of Environmental Chemical Transformation
The key enzymes involved in this process are the cytochrome p-450,
a collective term for a group of haemoproteins that bind foreign chemicals
(Xenobiotics) and transform their oxidation by inserting one molecule of oxygen
(O2) oxygenation. Such hydroxylation reactions convert many water insolubic
foreign compounds to more polar derivatives which are then more easily excreted.
Often associated with conversion to polarbolites is loss of pharmacologic or
toxicologic effects of drugs or other xenobiotics. These may serve as biomarkers
of exposure. Biomarkers of exposure have been the most actively studied especially
in the use of biomarkers of exposure to mutagenic and carcinogenic chemicals
(Anonymous, 1992). In general terms, markers of exposure rely on measurement
in body fluids or tissues of either the substance in question or its metabolites
or a product of a reaction with a biological molecule.
Biomarkers of exposure can be divided into markers of internal dose and markers
of effective dose. The former is an indicator of the occurrence and extent
of exposure of the subject, where as the latter is an indicator of the extent
of exposure of what is regarded to be the target molecule, structure or cell,
thus amenable to molecular epidemiology.
Biomarkers of internal dose indicate that exposure to a particular compound
has taken place by measuring the compound or its metabolites in body fluids.
Although human exposure to a particular chemical may be estimated from biomonitoring
studies using workplace monitoring for example or preferably personal monitors,
there is individual variability in absorption, distribution and excretion.
Consequently, it is preferable to measure the amount of compound or its metabolites
in a tissue or fluid from a subject in order to estimate the actual exposure
rather than the expected exposure.
Biomarkers of Oxidative Damage
Oxidative stress is a general term for a physiological or pathophysiological
situation in which oxidative processes exceed the antioxidant defences of an
organism. This principle has been utilized as selective and general biomarker
of oxidative damage to DNA. The production of free radicals has been shown
to be greatly increased to noxious environmental factors such as UV light,
cigarette smoke and environmental pollution. Super oxidedismutase (SOD) is
an enzyme used extensively as a biochemical indicator of pathological states
associated with oxidative stress (Autor, 1982) because of the protective role
it plays against deleterious effects triggered by superoxide anion in turn
arising from environmentally induced free radicals (Kehrer, 1993).
Molecular Epidemiology for an Environmentally Sustainable Future
The current education of most professionals involved in the management of
environmentally induced disorders is unquestionably incomplete. Cortese (1992)
has suggested that scientists are needed to understand the natural World, the
effects of human activity on the environment, the fate and transport of pollutants
in the environment, and the efficacy of environmental improvement strategies.
According to Cortese (1992) Health specialists on the otherhand, should help
understand the effects of environmental pollution on human health and advise
policy makers, patients, and the public on strategies to reduce health hazards.
This can better be achieved by early detection of pathophysiologic changes
employing molecular epidemiology. The multifactorial nature of toxic responses
to environmental chemicals necessitates the use of early biomarkers of effects
as well as biomarkers of exposure and susceptibility. It is essential that
all of us understand the importance of the environment to our existence and
quality of life and that we have the knowledge, tools, and sense of responsibility
to discharge our duties to society and thus ensuring a sustainable future.
Cautionary Note on the Use of Molecular Epidemiology
There is no doubt now that molecular epidemiology is sufficiently sensitive
and the preferred approach for the early detection of pathophysiologic response
to environmental toxicants and disease. It is however, worthy of note that
just because we can detect the presence of a chemical or measure a biochemical
effect does not mean that this represents a hazard and therefore that the individual
is at risk. Some biomarkers may be irrelevant to toxicity or too sensitive;
a good example of which is inhibition of the activity of the enzyme of the
haemopoietic system, d-aminolalvulinic acid dehydratase (ALA-D).
Part of this dilemma was about a decade ago revealed by the observation of
some investigators that it is becoming more difficult to distinguish between
measured alterations that are adaptive and reversible and those that are pathological
and irreversible (Timbrell et al, 1992). Therefore, different biomarkers need
to be used in conjunction where possible and appropriate. This is well illustrated
by lead exposure which has been well characterized in humans.
Conclusion
The nature of toxic substances that give rise to chronic poisoning varies
ranging from elements, particularly metals through complex organic and inorganic
compounds. These substances may be encountered as drugs, pesticides, industrial
chemicals and pollutants. Generally they constitute a spectrum of substances
in a variety of states in a multiplicity of matrices at extremely low concentrations.
Thus their ability to bring about pathophysiological changes is not immediately
evident. They constitute enormous challenges to both the analytical and clinical
toxicologist in search of biomarkers that will subsequently be employed in
molecular epidemiology. This ensures the early detection of biochemical lesions
that are related to subsequent changes in structure and physiology. Thus useful
as early indicators of environmental hazards that produce disease in humans.
This benefit will be greatly enhanced by the newer technologies of toxicogenomics
and metabonomics.
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