EU Research on Environment and Health - Results from projects funded by the Fifth Framework Programme Price excluding VAT in Luxembourg: EUR 25 Over ninety multidisciplinary pan-European
Trang 1EU Research on Environment and Health -
Results from projects funded by the Fifth Framework Programme
Price (excluding VAT) in Luxembourg: EUR 25
Over ninety multidisciplinary pan-European research projects dealing with environment
and health issues were funded by the European Commission’s Research
Directorate-General in the Fifth Framework Programme of Research (1998-2002) The results of
these projects have now become available and are presented in this catalogue The
projects presented addressed a multitude of issues ranging from health impacts of
exposure to electromagnetic fields to air pollution The results should be useful to many
stakeholders including the scientific community and policy makers
Trang 2Interested in European research?
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European Commission
Directorate-General for Research
Information and Communication Unit
Unit I5 – Climate change and environmental risks
Scientific Officer: Tuomo Karjalainen (Tuomo.KARJALAINEN@ec.europa.eu)
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Trang 3Directorate-General for Research
2007 Science, Economy and Society EUR 22816 EU
EU Research on
Environment and Health -
Results from projects funded by
the Fifth Framework Programme
ACKNOWLEDMENTS
The project related data was compiled for the most part by Dr Tuomo Karjalainen, European Commission,
Research Directorate-General, Directorate I (Environment), Unit Climate Change and Environmental Risks
(Head of Unit: Ms Elisabeth Lipiatou), with the skillful assistance of Ms Kerstin Johansson
Valuable contributions from the Directorate E (Biotechnologies, Agriculture, Food), Unit Food-Health-Wellbeing (Head of Unit: Antonio Di Giulio) are acknowledged, especially assistance from Drs Ana Nieto-Nuez and
Ebba Barany
Activities and contributions of former Scientific Officers in this field (including Mr Callum Searle, Dr Kirsi Haavisto,
Ms Minna Wilkki) should not be forgotten
The data in the project sheets was provided and validated for the most part by project coordinators and they bear responsibility for their scientific content and accuracy
Trang 4Europe Direct is a service to help you find answers
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The views expressed here are those of the authors and may not in any circumstances be regarded
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Cataloguing data can be found at the end of this publication
Luxembourg: Office for Official Publications of the European Communities, 2007
Trang 5Foreword
It is pretty much accepted in our society that
environmental factors such as noise or air pollution
can have an adverse impact on human health and
well-being Opinion polls show that the majority
of the European public has increasing concerns
about the influence of these factors on their health
and their children’s health in particular The links
between environmental factors and disease trends
are now being discovered through numerous
scientific research projects Amongst the links now
highlighted are:
Cancer rates, including children’s cancer, are
increasing by around 1% a year This increase
is believed to be linked, at least partially, to a
number of environmental pollutants;
Fertility rates are declining at a worrying rate in
some EU countries, and environmental pollution
is also partly suspected;
Neurodevelopmental disorders are on the
increase in our children (including conditions
such as autism) and environmental exposures
could play a role here;
Allergies and asthma are increasing by 5% a year
across the continent, and air pollutants could be
partly to blame;
In addition, new and emerging technologies and
societal challenges, such as widespread use of mobile
phones and the consequences of climate change,
could bring new long-term health consequences
that must be risk assessed and managed
The European Union has been at the forefront of research on the environment and health for many years Through successive European Research Framework Programmes and national science programmes, we have greatly increased our understanding of the complex links between environmental risk factors and their effects on the health of citizens, various vulnerable sections of society and the population as a whole
This accumulated scientific knowledge has helped shape national and EU policy initiatives designed to protect our environment and promote human health throughout the continent A good example of this is the European Environment and Health Action Plan adopted in 2004
This publication brings together the final results of all European-funded research projects in the field of environment and health from the Fifth Framework Programme of Research (FP5) Sponsored by the European Commission’s Directorate-General for Research, the projects covered a multitude of issues in this complex area I sincerely hope this comprehensive overview will allow you to find some answers to the many questions raised by the general public, scientific community and policy-makers on the links between environment and human health
Janez Potocnik Commissioner for Science and Research
Trang 7Table of contents
Air pollution-related health impacts 14
Chemicals and health impacts 20
Electromagnetic fields and health impacts .28
Noise-related health impacts .32
UV light and ionising radiation-related health impacts .34
Multiple stressors and factors and health impacts .36
Waterborne stressor-related health impacts 38
Climate change-related health impacts 40
Nanoparticle-related health impacts .42
Trang 8The most common diseases and medical conditions
that affect European citizens today result from a
combination of risk factors, which are both genetic
and environmental Some of these risks are well
established, whilst others are emerging as a result
of societal change
How specific health and medical issues affect
individuals varies with time, geography, even the
weather An individual’s vulnerability is determined
by genetic factors, age, their diet and health status
Assessing and managing the various established
and emerging risks to human health, inherent
in a modern, constantly evolving society, is an
immensely complex task But it is a vital task that
can improve the quality of life of all citizens and
protect public health
The need for research
Over the past few decades the role of environmental
factors has been highlighted in the health debate,
for example the role of environmental tobacco
smoke on increased lung cancer in non-smokers
and the possible implication of some chemicals
in the observed rise in testicular cancer in some
European countries The focus was initially on workplace exposures, but as many of these industrial risks have been recognised, understood, and effectively regulated, the focus has shifted to more widespread risks In particular, most recently, the role of environmental factors in the health of the young, even pre-natal, child has become a growing concern
Environmental pollutants such as tobacco smoke, asbestos, pesticides, traffic fumes, and heavy metals have all been linked to diseases like cancer, cardiovascular disease and abnormal pre- or post- natal development In addition, excessive exposure
to sunlight has been linked to cancer, while unhealthy nutrition can lead to heart disease Besides these effects, the noise of modern living can have serious health effects, including sleep disturbance and cardiovascular effects Allergies and asthma are
on the increase and the cost of their treatment is a significant strain on national medical budgets.New challenges are joining the old Climate change will effect our environment which in turn will present new health issues; new technologies such
as wireless communications and nanotechnology
could provide new potential for risk that must be assessed.The importance of environment-related disease and the need to reduce uncertainty regarding the health effects of environmental factors are clear The health and quality of life of European citizens would significantly benefit from reducing exposure
to key pollutants
Trang 9
have been implemented since 1984, but a specific
reference to concerns on the “personal environment”
first appeared in the third European Commission
Medical and Health Research Programme (MHR3) in
1982 to 1986 The subsequent MHR4 programme
(1987 – 1991) included “environment and
lifestyle-related health problems” in its priorities as well
as examining the effects of passive smoking and
exposure to industrial chemicals
The Biomedicine and Health Research programmes
BIOMED1 (1990 – 1994) and BIOMED2 (1994
– 1998) both covered environmental issues under
the theme “risk factors, especially in the context
of occupational medicine” and “diseases of major
socio-economic impact” In parallel, human health
issues were the subject of a number of projects
in the first and second “Specific Research and
Technological Development Programmes in the
field of Environment” ENV1 (1990 – 1994) and
ENV2 (1994 – 1998)
Environment and Health
issues in FP5
The Fifth European Community Research
Framework Programme (FP5) built on the results of
these previous initiatives through a number of more
integrated thematic programmes Environment and
health issues were mainly addressed within the
Quality of Life and Management of Living Resources
theme under Key Action 4 (KA4): Environment and
Health With a budget of €160 million over the
period 1998 – 2002, KA4 initiated more than 90
trans-national research projects the results from
which are presented together in this brochure for
the first time Projects were also funded by two
key actions within the Energy, Environment and
Sustainable Development programme
The general objective of environment and health
research in FP5 was to study the health effects of air
risks Special attention was paid to pollution in the workplace and to the effects on children and other vulnerable groups
The scientific and technological objectives were: Research into diseases and allergies related to, or influenced by, the environment, their prevention and their treatment;
The development of new methods of risk assessment, and of processes to reduce the causes and environmental factors which are harmful to health
Results of FP5 research - highlights
The research undertaken in FP5 consisted of nine priorities:
Air pollution-related health impacts Chemicals and health impacts Electromagnetic fields and health impacts Noise-related health impacts
UV light and ionising radiation-related health impacts
Multiple stressors and factors and their health impacts
Waterborne stressors and their health impacts Climate change-related health impacts Nanoparticles and health impactsThe first two priorities were the main focus of environment and health research for FP5, accounting for some 61 projects and 73% of the budget
Highlights of results for all priorities:
The adverse respiratory health effects of fine particles, nitrogen oxides and in particular smoking was repeatedly demonstrated The use of biomarkers to give early indication of either potential
to develop disease or evidence of exposure showed the utility of this emerging science for a variety of environmental stressors Effects were also observed
on other organs such as the cardiovascular system
Trang 10
These results have effectively fed into the EU policy
process on air pollution
Endocrine-related reproductive effects were
widely studied showing correlations between
exposure to a range of chemicals and adverse
effects in a variety of animal models ranging
from invertebrates to various mammals Human
studies showed, among others, that reproductive
health is deteriorating in several regions in Europe
as evidenced by declining sperm counts and
other parameters, but causes behind this change
remain unclear In addition, developmental and/or
neurobehavioural effects of some chemicals were
observed in animals as well as in exposed human
populations Studies on chemical pollution,
including how they are absorbed by the skin,
yielded new tools that will be of use in REACH
and workplace risk assessment
Fears about the adverse health effect of mobile
phone use and other electromagnetic sources were
not supported by research findings, although certain
genotoxic effects were seen in vitro, and the results
of some large-scale studies are still awaited
Clear evidence of links between transport noise,
classroom performance and health indicators
were made The additive effect of noise with
other environmental stressors was also clearly
demonstrated Noise can also have adverse
effects on the cardiovascular system
Genetic mechanisms for skin cancer development
were determined and biomarkers for early
diagnosis of UV damage identified
A major result of FP5 research was the development of
integrated environment and health risk assessment,
which was pioneered and shown to be effective
This approach paved the way for further more
extensive activity funded under the Sixth Framework
Programme of Research (FP6 – 2002-2006)
New technologies and methodologies were developed to help ensure the safety of bathing and drinking water across Europe
Initial work on the effects of global warming on diseases patterns and the potential effects of nanoparticles on human health was undertaken This work is continuing in FP6
In general, the knowledge gained from projects funded under FP5 helped to provide a scientific basis for assessing environmental risks, a main driver for developing knowledge-based policies
to protect public health
This research input is critical to good policy formulation across a wide range of areas including: The European Environment and Health Action Plan Sustainable Development Strategy
Thematic Strategy on Air Pollution Thematic Strategy on Urban Environment Community Strategy for Endocrine Disrupters GEOSS – Global Earth Observation System of Systems
REACH – Registration, Evaluation and Authorisation of Chemicals
Programme of Community Action in the Field of Public Health
EU Noise PolicyFull details of the research undertaken, its context, short project summaries and links to individual project sheets for all nine priorities can be found in individual chapters in this brochure
Continuing and future research
Following FP5, FP6 saw an increase in annual funding for Environment and Health projects from around €40 million a year to around €50 million for the period 2002 - 2006 The relevant funded projects were spread over four of the FP6 priorities: Food Quality and Safety1 (main area); Sustainable Development, Global Change and Ecosystems2;
10
1 http://cordis.europa.eu/food/home.html
2 http://cordis.europa.eu/sustdev/
Trang 11The first priority had a specific
‘Environmental Health Risks’
area, from which small and
large-scale research projects
and networks have been funded
related to many environment and
health issues such as cancer or
allergies/asthma A large majority
of these projects are ongoing
The Sustainable Development,
Global Change and Ecosystems
priority devoted a large effort on
the improvement of integrated
environment and health risk
assessment as well health impact
assessment including valuation
and cost/ benefit analyses were
also funded in the Scientific
Support priority Genomics and
Biotechnology for Health sponsored epidemiological
and toxicological studies as well as projects related
to alternatives to animal testing Finally, the so-called
‘Priority 8’ (Scientific Support to Policy) has funded
a number of research projects with direct relevance
to policy making
One of the main drivers for research in FP6 was the
European Commission’s Environment and Health
Action Plan, adopted in 20045 The plan aims to
improve our understanding of the links between
environmental factors and health It was partially
inspired by a need to more fully engage policy
with new research results coming out of FP5 and
its precursors Implementation of the Action Plan’s
goals was started with FP6 via the funding of several
large projects referred to above
FP6 also saw the introduction of integrated
environment and health risk assessment
learnt in FP5 about the complexity and interaction between risks It also offers a better way to link environment and health data in a manner that supports policy-making This is also a systematic approach, incorporating the identification
of pollution sources, exposures (including the use of human biomonitoring pioneered
in FP5), making links with health effects, and economic valuation The development
of economic valuation models and tools for assessing the impact of policies is a vital link for effective regulation
Although funding for environment and health issues was higher in FP6, there were fewer projects, though this was compensated by their size In FP6,
an increased emphasis was put on integrated risk assessment, as described above, and multiple stressor effects Less funding was given to environmental stressors such as noise, air pollution and electromagnetic fields in FP6 as the results from ongoing projects in FP5 were awaited in order to direct further research In addition, projects covering risk/ benefit and cost/ benefit gained in importance
as did those relating to climate change – an area that had first been investigated during FP5
We are now entering FP7, which was launched at the beginning of 2007 This seven-year programme sees
a significant boost in overall funding and environment and health is identified as one of three activities under the theme “Environment (including Climate Change)”
of the Cooperation Programme6
Trang 12Three priorities have been identified for environmental
and health activity:
Health effects of exposure to emerging
environmental stressors
Climate change and health
Novel approaches to environment and health risk
assessment
Other FP7 themes – in particular “Health” and
“Food, Agriculture, Fisheries and Biotechnology”
– will complement environment and health activities
and there may be opportunities for joint calls
FP5 was an important precursor in the field of
environment and health, delivering new knowledge,
pointing the way for further research and setting the
basis for policy-making However, a lot of information
on how environmental factors interact with human
health is still required In many ways the more
answers we find, the more questions we generate!
The integrated approach, focusing on multiple
stressors, pathways and effects, will be particularly
valuable in yielding definitive insights on the extent
to which environmental factors impact our health at
both the individual and societal levels
Environment and health
issues: joint effort at EU
and global levels
Reflecting the complexity
of issues involved, the
actors involved at the
Community and global level
are numerous As regards
FP5 and FP6, within the
Research
Directorate-General, two directorates
were chiefly involved with
sponsoring environment and health-related
research activities: Directorate E (Biotechnologies,
Agriculture, Food) and Directorate I (Environment)
In FP7 Directorate I is taking the lead, with the Health and Food Directorates playing a lesser role DG Information Society and Media will also fund research in this area, for example concerning personal exposure monitoring
Other European actors that play significant roles
in environment and health issues are DG Joint Research Centre7, the European Environmental Agency (EEA)8 and the European Food Standards Agency (EFSA)9 EEA and EFSA have been important end-users of research funded by the Framework Programmes
The main policy-making Directorate-Generals that benefit from the research input are Environment10, Health and Consumer Protection11 and Enterprise12.European research also interacts with other national and international endeavours In particular, the European Commission works actively with bodies such
as the World Health Organisation (WHO) on initiatives like the Children’s Health and Environment Action Plan for Europe (CEHAPE)13 and the Organisation for Economic Co-operation and Development (OECD) Task Force on Endocrine Disrupters
Trang 14Air pollution-related
health impacts
European context
Although for most parts of Europe dense industrial
“smog” is no longer a common feature of our
larger cities due to various clean air regulations, air
pollution, though less visible, is still a major health
hazard In particular the significant recent increases
in traffic volumes has brought with it new risks
Air pollution includes dust, smoke and gases
in the air that we breathe Such pollution can
have natural sources like volcanic eruptions or
traditional agricultural practices, but the main
day-to-day contributors are from traffic and
industry In addition to outdoor pollution, there is
also indoor pollution, with a long list of potential
contributors These include: ambient air pollution,
dust, inefficient combustion of fuel for cooking and
heating, household chemical products, fabrics and
coverings, and, in particular, tobacco smoke
Air pollution can be harmful to all the vital organs
of the human body It can penetrate the lungs and
transfer into the blood system moving around the
body through the blood vessels to the heart and into
the immune system This means that air pollution
does not only aggravate respiratory problems and can
cause asthma and other allergic responses, but can
also be involved in cardiovascular health problems
The net result is that in cities across Europe, air pollution may be causing tens of thousands of premature deaths from respiratory and cardiovascular diseases annually Indoor and outdoor air pollution are the environmental factors with the greatest impact
on general health in Europe and are responsible for the largest burden of environment-related disease.Recent estimates indicate that 20 million Europeans suffer from respiratory problems every day14 Particulate matter and especially small particles with diameter less than 2.5 micrometres (μm) – also known as PM2.5 – are associated with increased mortality, especially from cardiovascular and cardiopulmonary diseases
Asthma is increasing all over Europe, although the rate of increase has considerable variation across the continent The cost to European society of asthma is estimated at €3 billion per year15 The annual increase of childhood asthma/allergy cases in Europe is estimated
at 5%; thus by 2050 one out of two European children will be likely to suffer from allergic disease
FP5 projects – Revealing the link between air pollution and health
Among the environment and health projects funded
by FP5, the 20 projects listed here are related directly
Air Pollution-Related Environmental Stressors
Common outdoor and indoor pollutants include:
Gases such as ozone, carbon monoxide, nitrogen oxides, sulphur dioxide;
Particulate matter, mineral ash, smoke, and engine exhaust fumes; and
Tobacco smoke, dust containing various allergens, substances emanating from building materials
and consumer products
14
14 “Environment and Health”, EEA Report No 10/2005 http://reports.eea.europa.eu/eea_report_2005_10/en/EEA_report_10_2005.pdf
15 “Environment and Health”, EEA Report No 10/2005 http://reports.eea.europa.eu/eea_report_2005_10/en/EEA_report_10_2005.pdf
Trang 15health effects and provide tools
for measuring real life exposures
and effects The projects
favoured the development
of protective measures and
have fed into the process of
regulating pollutant emissions
European Commission funding
for these projects represented
around 17% of the total budget
allocated to environment and
health in FP5
Research results
The FP5 projects undertaken in this area can be
classified into four groups:
Air pollution and respiratory health – 11 projects
Air pollution and carcinogenic or genotoxic
The findings of research on respiratory health
highlighted correlations between asthma and
allergies and cooking with gas, smoking and some
domestic cleaning sprays In particular ensuring
adequate ventilation for domestic gas cookers
to reduce ambient nitrogen oxides could have a
significant impact on indoor air quality
The invasive nature and damage caused by small
particles (PM10, PM2.5 etc.) in the lungs and other
areas of the body were extensively investigated
Although particle samples vary widely across
Europe, correlations between inflammatory lung
responses and particle pollution were observed and
also related to genotoxicity Some particles were
found to have high poly aromatic hydrocarbon and/
or arsenic content
All the projects accumulated further evidence that reinforces the need to regulate to reduce the concentration of these particles being produced by human activities – in particular those emanating from diesel transport Smoking and the use of solid fuel for residential heating were also significant sources.The emerging science of biomarkers was shown
to be very useful as a method for the early diagnosis and assessment of respiratory disease New methods were developed to rapidly identify potential exposure to occupational allergens New accurate calibration methods for lung diagnostic equipment will also help medical intervention and clinical support in this area
The potential for carcinogenic activity of polycyclic aromatic hydrocarbons was demonstrated including DNA damage and inhibition of repair processes; similar DNA damage was also observed for smokers Detrimental genotoxic effects of environmental pollution were also shown in children with chromosomal aberrations most affected by chemical pollution whilst other genetic effects were influenced
by environmental tobacco smoke and smoking during pregnancy Adverse genetic and carcinogenic effects of traffic pollution were found, in particular for ex-smokers (up to 10 years after quitting the habit), and further evidence for the undesirable health effects of environmental tobacco smoke
1
Trang 16Further evidence to assist regulation of vehicle fuel
was found when investigating cardiovascular effects
There was some contradictory evidence on the
effects of particles effects, however high sulphur fuels
– now effectively regulated out of the transport market
– were shown as a primary trigger for DNA damage
The significant impact of fine airborne particles and
ozone leading to increasing premature death gave
further evidence for regulation and preventative
measures, while new markers for and understanding
of mercury exposure will help public protection
Further work
Health-related air pollution research in FP6 is focused
in three ongoing projects ENVIE16 (a coordination
action on indoor air quality and health effects),
PRONET17 (Policy reductions option network that
will exchange useful practices at a regional level
on indoor air quality and road traffic hazards), and
CAIR4HEALTH support action (Clean Air for Health
– research needs for sustainable development
policies)
Air pollution also features as an aspect of the large
integrated risk assessment project INTARESE18
(integrated assessment of health risks of
environmental stressors in Europe) and a variety of
other such projects
For FP7, research on air pollution-related activities
may be funded under the Health (cohort studies),
Information and Communication Technologies
(personalised exposure measurement devices) and
Energy and Transport themes However, the main
focus of activity concerning health impacts of air
pollution will be the Environment (including climate
change) theme19
FP5 projects list
Brief details of each project in this area are given
below For more details please see the individual
project summary sheets
Air Pollution and Respiratory Health
AIRALLERG – Effects of Outdoor and Indoor Air Pollution on the Development of Allergic Disease in Children
Variations in levels of indoor nitrogen dioxide (NO2) and nitrous acid (HONO) were correlated with use
of gas for cooking and smoking; other correlations included floor type with levels of floor dust amounts
BIOAIR – Longitudinal Assessment of Clinical Course and Biomarkers in Severe Chronic Airway Disease
This in-depth study has provided new insights on the mechanisms involved and interventions possible for patients suffering these widespread debilitating
HELIOS – Biomarkers for the Non-invasive Assessment of Acute and Chronic Effects of Air Pollutants on the Respiratory Epithelium
No evidence of chronic toxic effects on lung function that correlated with differences in air quality across Europe was found In particular no effect due to ozone However, trichloramine above a certain threshold has major effect on children’s lungs
[Page 50]
HEPMEAP – Health Effects of Particles from Motor Engine Exhaust and Ambient Air Pollution
Particulate matter collected in this project varied widely across Europe but coarse and fine particles appear to have similar toxic effects when compared
Trang 17variety of allergens: nasal sampling of employees
was shown as a feasible approach for short-term
measurements and a lateral flow immunoassay was
developed as a rapid test method for occupational
PAMCHAR – Chemical and Biological
Characterisation of Ambient Air Coarse, Fine
and Ultrafine Particles for Human Health Risk
Assessment in Europe
High PM10-2.5 concentration in samples correlated
with strong inflammatory lung responses; increased
health risks were suggested in communities with
heavy use of solid fuel for residential heating
[Page 56]
PATY – Pollution and the Young: Combined
Analyses of Cross-sectional Studies of
Respiratory Health of Children and Air Pollution
Uncertainties remain about the impacts of air
pollution on the young By bringing together a large
number of comparable data, which have already
been collected, this study offers a cost-effective
route to improved assessments of the effects of the
long term impacts of air pollution using data from
12 countries and a combined study size of over
PAWG –Programmable Air Wave Generator with
Controlled Temperature, Pressure, Humidity and
Air Wave Frequencies for Calibration
This project has developed new methods and tools
for accurate calibration of lung diagnostic and other
medical equipment This is important for efficient
and effective diagnosis and treatment [Page 60]
RAIAP – Respiratory Allergy and Inflammation
due to Ambient Particles – A Europe-wide
Assessment
Chemical characterisation of fine and coarse
samples showed distinct differences across
Europe and allergy and inflammation responses were measured – the inflammation response was greatest for coarse samples [Page 62]
RUPIOH –Relationship between Ultrafine and Fine Particulate Matter in Indoor and Outdoor Air and Respiratory Health
It was found that using a central urban sampling point allowed a good estimate for temporal distribution across a metropolitan area; little difference in particle concentration between central and suburban outdoor sites was found, but there was little correlation between outdoor and indoor air concentrations
[Page 64]
1
Trang 18Air Pollution and Genotoxic or
Carcinogenic Effects
AMBIPATH – Mechanism-based Approaches to
Improved Cancer Risk Assessment of Ambient
Air Polycyclic Aromatic Hydrocarbons (PAHs)
The mutagenic potency of PAHs was found to parallel
their carcinogenic potency and mixture studies show
evidence of additive effects - in some cases at doses
close to those of environmental relevance [Page 66]
CHILDRENGENONETWORK – European
Network on Children’s Susceptibility and
Exposure to Environmental Genotoxicants
Age and exposure-related increases in a number of
cytogenetic endpoints in children with increase in
environmental pollutants (chemicals and tobacco
EXPAH –Effects of PAHs in Environmental Pollution
on Exogenous and Endogenous DNA Damage
DNA adducts were found to be more abundant in
exposed population (compared to control group)
and exposure to PAHs significantly influenced the
DNA repair process in the subjects’ lymphocytes
[Page 70]
GEN-AIR – Molecular Changes and Genetic Susceptibility in Relation to Air Pollution and Environmental Tobacco Smoke: a Case-Control Study in Non-smokers Nested in the Epic Investigation
High exposure to traffic pollution increased potential for lung cancer in ex-smokers with no observable effect on people who had never smoked; in addition, DNA adducts seem to be associated with subsequent risk of lung cancer [Page 72]
Air Pollution and Cardiovascular Effects
AIRGENE – Air Pollution and Inflammatory Response in Myocardial Infraction Survivors: Gene-environment-interactions in High-risk Group
No association was found between ambient air pollution and risk indicators for heart attack, suggesting that medication, such as statins, may
be acting protectively and susceptibility was heavily related to personal characteristics [Page 74]
HEAPSS – Health Effects of Air Pollution on Susceptible Subpopulations: Ultrafine Particles and Myocardial Infarction
This study did see a relation between air pollution and heart attacks although results with mortality were less consistent: total particle number and carbon monoxide concentration were the most strongly related with the health effects studied [Page 76]
MAAPHRI – Multidisciplinary Approaches to Airborne Pollutants Health-Related Issues
High sulphur fuels were shown to
be the main toxic component to trigger DNA damage and systemic inflammation A new danger with increased NO2 emissions was identified that can trigger acute cardiorespiratory impacts [Page 78]
1
Trang 19and Health
Impact assessment revealed that ozone and fine
air particle pollution could result in several tens to
hundreds of thousands of premature deaths each
EMECAP – European Mercury Emission from
Chlor-alkali Plants
This study has increased our knowledge of
environmental exposure to mercury, identified markers
for early biological effects and developed innovative
analytical devices for large area monitoring
[Page 82]
1
Trang 20Chemicals
and health impacts
Friends or foe?
HPC - Halogenated Phenolic Compound
PAH - Polycyclic Aromatic Hydrocarbon
PCB - Polychlorinated Biphenyl
POP - Persistent Organic Pollutant
NO2 - Nitrogen dioxide
European context
Chemicals are ubiquitous Everything in our
world is made of chemicals including all living
organisms, our food and the air we breathe
Our environment and ourselves are essentially
a complex, interacting mixture of chemical
molecules In addition to natural environmental
chemicals, human activity and ingenuity has
added new synthetic molecules
This technological advance has done much to
enhance European quality of life over the last
century, but has resulted in the release of many
potentially toxic substances into the environment,
some of which contaminate the air and soil, and
find their way into ground and coastal waters
Chemicals enter our environment through many human activities Mining sites can release heavy metals, acids and organic compounds Combustion plants, waste incinerators, heating systems and the internal combustion engine emit acid gases, ozone precursors and persistent organic pollutants such
as dioxins and furans Mercury and volatile organic compounds can evaporate from old industrial sites Industries and households discharge chemicals – including synthetic hormones derived from the wide-scale use of the birth control pill – into sewers and thus into rivers Farmers use synthetic fertilisers and pesticides over large areas In and outside our buildings, at home, work or play, our materials, furnishings and fibres are all coated with paint, flame retardants and fungicides
Once chemicals are in the environment they can move around by a variety of mechanisms Some react with light or other chemicals, some are degraded, but others persist for many years Following ingestion by living organisms some chemicals can become
‘bio-accumulated’ and become more concentrated as they move
up the food chain Unexpectedly high (and toxic) concentrations
20
Trang 21as the Arctic and Antarctic.
More than 10 million individual chemicals have been
identified, of which some 100 000 are registered in
the European Union and about 30 000 of these are
used regularly in industrial processes Some are
known to be harmful to humans, wildlife and/ or the
environment, but for others toxicity and ecotoxicity
data are not readily available
FP5 projects –
Towards a better understanding
Understanding the effects of chemical contaminants
on human health was a major priority for FP5 and a
significant minority of all projects in the Environment
and Health area were tasked to investigate this area
Some focused explicitly on the chemicals and many
more examined their effects and interactions
The projects focused on a number of issues:
Hazard and risk characterisation of various
groups of chemicals including heavy metals,
endocrine disrupters (please see box on
Endocrine Disrupters), dioxins, PCBs, styrene,
and asbestos;
Epidemiological approaches to exposure
assessment including the use of biomarkers,
birth cohorts etc.;
Development of new methods and tests for
analysis of toxicity;
Exploring the role of genetic susceptibility in
disease development;
Investigation of mechanisms of disease development
in various organs in ‘real life’ exposure situations,
i.e., low doses and multiple exposures
European Commission funding for these projects
represented over 50% of the total budget
allocated to environment and health in FP5 In
fact, around 20% of the budget was allocated
to investigation of projects focused on endocrine
Endocrine-related reproductive effects were widely studied showing correlations especially between exposure to a variety of chemicals and reproductive parameters in a variety of animal models and also
in human studies In particular, a significant new hypothesis called testicular dysgenesis syndrome was developed that provides an explanation for
a plausible link between environmental factors including endocrine disrupting chemicals and the
21
with the functions of the endocrine (or nal) system of organisms Chemicals that exhibit endocrine disrupting activity can be natural or synthetic hormones or other natural or synthetic chemical compounds Potential endocrine dis-rupters include the synthetic chemicals: polychlo-robiphenyls, dioxins, persistent pesticides and some chemicals used in the plastics and deter-gents industry
hormo-Potential health effects of endocrine disrupters include breast, prostate and testicular cancer, urogentital malformations and reduced male fer-tility Exposure in children may affect thyroid and immune systems and alter physical and mental development Endocrine disrupters can have a significant effect on the health of humans and other organisms, so represent a major, medical, environmental and social concern
Trang 22observed medical outcomes such as reduced
semen quality or testicular cancer
Neurobehavioural effects of some chemicals were
observed In particular, elevated polychlorinated
biphenyl (PCB) serum concentration was correlated
with poor sensomotor function in children In
contrast other studies, found no ill effects and/
or unacceptable exposures for brominated
halogenated phenolic compounds and pesticides
Some potential androgenic/ anti- androgenic
chemicals were shown to have clear effects in animal
models including invertebrates but acceptable daily
dietary intake levels for humans were not found to
be exceeded in Europe
The carcinogenic risk of arsenic was investigated,
mechanisms for its effect on DNA proposed and a
lower limit for impact due to oral exposure determined
New biomarkers for cancer were established
including early identification of high risk individuals
Potential health risks from wood dust were assessed
and molecular mechanisms proposed
Asbestos-substitute materials were evaluated and while all
samples could induce markers for lung inflammation
two showed potential genotoxic effects
Chemicals that interfere with cell division were
studied and a battery of new tests to determine the
biological and health significance of such chemicals
developed – the same study found that current
levels of exposure to bisphenol A in Europe did not
represent a significant health threat Encouraging
data showing reduced workplace exposure to
process dust in the rubber industry was also found
Work on multiple effects of chemicals focused, among
others, on dioxin which highlighted developmental
effects (such as tooth development) as highly
sensitive while cancer effects were less sensitive
than previously believed Work on multiple effects of
endocrine disrupters gave contradictory results with
some research demonstrating no morphological
effects, while others found effects, elaborated
mechanisms and proposed risk assessments for non-reproductive organs in humans
New methods such as bioassays and models such as transgenic animals for risk assessment provide valuable tools and can give new insights on mechanistic effects New methods for estimating the effects of endocrine disrupting mixtures, biomarkers and other methods for endocrine detection and characterisation, and effects of endocrine active substances on bone development were developed Better prediction of pesticide concentrations
in the environment and their detection with biosensors was demonstrated Studies of how chemicals are absorbed by the skin also yielded new tools that will be
of use in REACH and workplace risk assessment.Other new predictive method development included new “DNA chip” technology for immunotoxicity testing, fragrance allergy testing that reduced animal use and provided more information on sensitisers, neurotoxic effects of volatile chemicals and biomonitoring for occupational exposure to styrene The effect of toxic metals and insecticides
on the immune function, pregnancy and foetal development was also studied
Further work
Considerable resources continued to be invested in research on chemicals and health during FP6 and will continue during FP7 Focus is shifting in particular on early exposures to multiple chemicals and their long-term health impacts in vulnerable populations such as children New efficient methods for genotoxic analysis and methods for risk assessment of chemicals – in
particular computational or in vitro methods – that
reduce, refine or replace the use of animal testing are
of particular interest both to gain new knowledge and
as supports to significant new chemicals regulation (REACH) aimed at increasing public safety
FP5 projects list
Brief details of each project in this area are given
on the next page For more details please see the individual project summary sheets
22
Trang 23Chemicals with Reproductive and
Developmental Effects
ANEMONE –Assessment of Neurobehavioural
Endpoints and Markers of Neurotoxicant
Exposures
PCB concentration in children from the Faeroe islands
were on average 60% those of their mothers but
this increased with duration of breastfeeding Their
performance in neurobehavioural tests decreased with
the extent of exposure to prenatal methyl mercury
[Page 84]
BEEP – Biological Effects of Environmental
Pollution in Marine Coastal Ecosystems
A range of biomarkers were developed to evaluate
pollutant effects on the reproductive health of mussels
and fish to give a standardised array of biomarkers
for use in international monitoring programmes
[Page 86]
BIOCET – Bioaccumulation of Persistent
Organic Pollutants (POPs) in Small Cetaceans
in European Waters: Transport Pathways and
Impact on Reproduction
POP levels in female common dolphins were linked to
diet, area and reproductive status; POP concentrations
were commonly recorded above levels where effects
on reproduction would be expected [Page 88]
Mixtures of Organohalogens
The study concluded that there is a sufficient margin of safety for brominated HPCs (halogenated phenolic compounds) and current exposure of humans to such HPCs does not pose any risk for
COMPRENDO – Comparative Research on Endocrine Disrupters: Phylogenic Approach and Common Principles focusing on Androgenic/ Anti-androgenic Compounds
The level of contamination of food by pesticides, organochlorine and organotin compounds was found not to exceed Acceptable Daily Intake levels; however, observations of the effects of these chemicals on a variety of animal models has resulted in some new Predicted No Effect Concentrations for risk assessment [Page 92]
ENDISRUPT – Identification of Critical Rat Testicular Genes altered after Fetal Androgenic Disruption by Flutamide: Use of DNA Microarray
This project showed that in utero exposure to anti-androgenic chemicals induced long-term programmed cell death in testicular germ cells A health risk associated with foetal exposure to such endocrine disrupters was suggested [Page 94]
ENDOMET – Dysregulation of Endogenous
Steroid Metabolism Potentially alters Neuronal and Reproductive System Development: Effects
of Environmental Plasticisers
A number of plasticisers were demonstrated to have
a variety of effects on gene regulation, cell signalling
and reproduction The project provided new in vitro test protocols that can identify the endocrine
disrupting potential of chemicals [Page 96]
ENV REPROD HEALTH – Increasing Incidence
of Human Male Reproductive Health Disorders
in Relation to Environmental Effects on
23
Trang 24Growth- and Sex Steroid Induced Alterations in
Programmed Development
The project showed significant differences in
sperm quality between countries (Denmark and
Finland) with differences reflecting incidence of
testicular cancer and other genital malformations A
significant new hypothesis was proposed: testicular
EUROPIT – Toxicological Evaluation of the
Immune Function of Pesticide Workers, a
Europe-wide Assessment
No clinical effects of exposure to pesticides were
observed although some subtle immune alterations
EXPORED –Multi-organic Risk Assessment of
Selected Endocrine Disrupters
Analysis showed that exposure to PBDE
(polybrominated diphenyl ethers) was associated
with increased risk of the male genital malformation
cryptorchidism Associations with other individual
chemicals were not clear but a combined statistical
analysis of the eight most abundant persistent
pesticides showed levels in breast milk were
significantly higher for boys with cryptorchidism
[Page 102]
FIRE –Risk Assessment of Brominated Flame
Retardants as Suspected Endocrine-Disrupters
for Human and Wildlife Health
Tetrabromobisphenol A (TBBPA) is known to act on
the thyroid gland accompanied by neurobehavioural changes, this project demonstrated endocrine disrupting activity in both human and fish subjects
[Page 104]
GENDISRUPT – Genetic Markers and Susceptibility to the Effects of Endocrine Disruptors during Mammalian Testis Development
Extensive microarray analysis of the genetic effect
of selected endocrine disrupters on testicular cells showed that mono ester phthalate (MEHP) produced the highest deregulation The findings support a genetic basis for human male infertility and the
project developed an in vitro assay to identify and
quantify estrogenic activity of endocrine disrupters
[Page 106]
INUENDO – Biopersistent organochlorines
in Diet and Human Fertility Epidemiological Studies of time in Pregnancy and Semen Quality
in Inuit and European Populations
Concentration of polychlorinated biphenyls (PCBs)
in serum related to reduced fertility in Greenland but not in Caucasian couples High PCB exposure associated with 50% increase in sperm with damaged DNA in Caucasian males; however, no correlations were seen between fertility and other chemicals including POP markers [Page 108]
PBDE-NTOX – Developmental Neurotoxicity
of Polybrominated Diphenyl-ethers (PBDE): Mechanisms and Effects
The project demonstrated a link between gestational or early postnatal exposure to PBDE and interference with a number of neurobehavioural
PCBRISK – Evaluating Human Health Risk from Low-dose and Long-term PCB Exposure
A Slovakian child cohort showed significant associations between PCB serum concentrations and performance in sensomotor tests Significant effects also demonstrated on thyroid activity, tooth
24
Trang 25Molecular Epidemiology
Positive association was found between exposure
to arsenic and three types of cancer: basal cell
carcinoma of the skin is associated with lifetime
average arsenic concentration, bladder cancer with
cumulative arsenic dose, and kidney cancer with
ASRISK –The Mechanistic Basis for providing a
Realistic Cancer Risk Assessment for Exposure
to Inorganic Arsenic within the European
Community
Human studies showed that induction of micronuclei
in human white blood cells was the most sensitive
biological indicator for oral exposure to arsenic The
project also shed light on the mechanism by which
arsenic disrupted DNA repair and other processes
CANCERRISKBIOMARKERS – Cytogenetic
Biomarkers and Human Cancer Risk
The frequency of chromosomal aberrations was
shown to be a potential biomarker for cancer, in
particular for stomach and colorectal cancers The
project also suggested that frequency of micronuclei
may have value as a predictor [Page 118]
EXASRUB – Improved Exposure Assessment
for Prospective Cohort Studies and Exposure
Control in the Rubber Manufacturing Industry
This comprehensive database shows a clear
downward time trend for inhalable and respirable
rubber process dust with average occupational
exposure in most European countries now below
FIBRETOX –Mechanisms of Toxicity of
Asbestos-Substitute Mineral Fibres: New Approaches to
Hazard and Risk Assessment
All four fibres tested could induce changes in
early biomarkers for lung inflammation, but only
two (amosite, RW1) induced potential persistent
OXEXRISK – Oxidative Stress and Chronic Diseases: Exocyclic DNA Adducts as Markers for Disrupted Genomic Integrity and Risk
The project provided further validation for the use
of etheno-adducts as promising biomarkers in aetiology and cancer prevention research including early identification of risk groups or individuals
WOODRISK –Risk Assessment of Wood Dust: Assessment of Exposure, Health Effects and Biological Mechanisms
Wood dust appears to induce pulmonary inflammation processes, generate reactive oxygen species and genotoxic effects The project also gave estimates of current workplace
Chemicals with Multiple Effects ESTROGENS & DISEASE – The Impact
of Developmental Exposure to Weak (Environmental) Estrogens on the Incidence of Diseases in Target Organs later in Life
Although no significant morphological effects of oestrogen exposure in testis, ovary, prostate, brain or mammary glands was found, the general conclusion was that exposure to low dose oestrogen before birth can cause subtle, long-term changes in the expression of specific genes and proteins
[Page 130]
2
Trang 26EURISKED –Multi-organic Risk Assessment of
Selected Endocrine Disrupters
The effects of endocrine disrupters including
UV-sunscreen formulations were studied in a number
of organs including the thyroid, liver and the brain
[Page 132]
Chemicals: Risk Assessment,
Testing and Models
ACE – Analysing Combination Effects of
Mixtures of Estrogenic Chemicals in Marine and
Freshwater Organisms
Validated prediction concepts have used
concentration addition to accurately predict the
effect of mixtures of environmental oestrogens
This has implications for current risk assessment
which should be revised to increase protection of
APECOP – Effective Approaches for Assessing
the Predicted Environmental Concentrations
(PEC) of Pesticides: a Proposal supporting the
Harmonised Registration of Pesticides in Europe
A spatially distributed modelling approach allowed
introduction of a more detailed description of
variability in soil, crop and climate in ground-water
exposure in PEC assessment [Page 136]
BONETOX – Bone Development and
Homeostasis: Critical Targets in Toxicology
Research to Support Test-method Development
and Human-health Risk Assessment for Dioxins
and other Endocrine-disrupting Compounds in
the Food Chain
This project is investigating the mechanisms of
chemically-induced bone and embryo toxicity The
contribution of endocrine disrupting chemicals to
increasing levels of osteoporosis and other bone
disorders will be estimated [Page 138]
DIOXIN RISK ASSESSMENT –Comprehensive
Risk Analysis of Dioxins: Development of
Methodology to Assess Genetic Susceptibility
to Developmental Disturbances and Cancer
Dioxin effects can be divided into two types with
important implications for risk assessment: Dioxin type I are low dose effects that follow reasonably predictable dose ranges with biochemical effects, including teeth defects, whilst Type II effects are variable inter-species due to high dose and include wasting syndrome, liver damage and (probably) cancer Risk assessment should be based on developmental (type I) effects rather than cancer
[Page 140]
EASYRING –Environmental-agent Susceptibility Assessment Utilising Existing and Novel Biomarkers as Rapid Non-invasive Testing Methods
Fish from polluted river water were found to tend towards increasing levels of vitellogenin (VTG), a biomarker for oestrogenicity, and liver and gonad morphological effects New non-invasive tests for VTG and computational (QSAR) models to predict the endocrine disruptive potential of chemicals
EDEN –Endocrine Disrupters: Exploring novel Endpoints, Exposure, Low-dose and Mixture Effects in Humans, Aquatic Wildlife and Laboratory Animals
This wide-ranging project is trying to determine
if current hazard and risk assessment strategies
to deal with endocrine disrupters in Europe are sufficient to protect both humans and wildlife – results on mixtures already indicate an area for potential revised regulation [Page 144]
EDERA – Development and Implementation
of New in vivo and in vitro Systems for the
Characterisation of Endocrine Disrupters
By developing ‘reporter mouse’ imaging technology this project provided a more refined method for studying effects of endocrine disruption whilst reducing the number of animals required for testing and eliminating the need for experimental animals to
EDETOX – Evaluations and Predictions of Dermal Absorption of Toxic Chemicals
26
Trang 27dermal penetration of a chemical based on its
physicochemical properties [Page 148]
FRAGRANCE ALLERGY –Fragrance Chemical
Allergy: a Major Environmental and Consumer
Health Problem in Europe
A number of new fragrance allergens were identified
and new tools to identify fragrance sensitisers
and fragrance sensitive persons were developed
together with suggestions for safer substitute
IMMUNOTOX CELL CHIP –A new Technology for
Fluorescent ‘Cell Chip’ Immunotoxicity Testing
A high throughput screening test based on a
fluorescent cell chip technology using changes in
cytokine expression in an in vitro test to determine
in vivo perturbation potential in the immune system
MENDOS – Biomimetic Optical Sensors for
Environmental Endocrine Disruptor Screening
The basis for producing high throughput
biomimetic and biological sensors for endocrine
disruptor activity was established for fully functional
molecularly imprinted polymer (MIP) technology
[Page 154]
Amongst other finding the project showed that in utero environmental exposure to toxic metals and organochlorine insecticides influenced immune function in placental tissue, maternal and cord blood and such compounds can cross the placenta
in vivo and accumulate in foetal organs.[Page 156]
RANTIV – Development of Methods for Predictive Toxicity Testing with Reference to Neurotoxic Volatile Chemicals
New in vitro tests were developed that can predict
neurotoxic effects and are especially good for
understanding mechanism of action However, in vivo
exposures followed by behavioural analysis are still required to detect subtle toxic effects [Page 158]
RISKOFDERM – Risk Assessment for Occupational Dermal Exposure to Chemicals This project delivered two major outputs: a predictive dermal exposure model that will be of use in implementation of REACH and a tool kit for risk assessment and risk management of dermal
[Page 164]
2
Trang 28Electromagnetic fields
and health impacts
What are electromagnetic fields?
Electric fields are measured in volts per metre and are generated by any electric charge The strength of an electric field decreases with distance from its source and can be blocked by walls and other intervening materials Magnetic fields are measured in Tesla (T) and generated by any magnetic object or a moving electric current They also decrease with distance from the source but are less shielded by intervening objects
Electric and magnetic fields are linked as whenever an electric current moves in an electric field then a magnetic field in generated, similarly if a magnet moves in a magnetic field it can induce an electric field This electromagnetic phenom-enon has brought many benefits to society in terms of electrical appliances and other specific use of electromagnetic fields for medical and other applications
Electromagnetic fields (EMF) can be described as a wave that oscillates at a particular frequency Frequency is ured in hertz (Hz or oscillations per second)
meas-European context
Electric and magnetic fields are all around us in
modern society, but are also a feature of nature
Lightening is the result of the build-up of an electric
field resulting in a discharge of current – the
lightening bolt The Earth itself has a well known
magnetic field that humans (and other animals) have
found so useful to help navigation over the years
Human-produced sources of EMF are now
everywhere in our homes, schools and workplaces
An EMF is generated whenever an electric current flows, so every time you operate an electrical appliance you also produce an EMF Using the hairdryer, the vacuum cleaner, the microwave and the TV remote all generate EMF
In the street radio-frequency antennae, cabling for power supply and other uses ensures the presence
of EMF, while at the office the computers and their screens, electric motors and security devices keep
us bathed in an unseen, but weak, EMF
The number and variety of EMF frequencies experienced in society is increasing all the time with new technologies such as Wi-Fi and Bluetooth producing new wide-spread sources.Mobile phones are a particular source of EMF that has grown rapidly and brought benefits
to our lives It also brings two potential sources of EMF: the
2
Trang 29body, in particular the head, during use.
When an EMF interacts with living cells and tissues
this can cause heating, alter chemical reactions, or
induce electrical charges and currents All of these
interactions could potentially produce adverse
health effects There have been suggestions
of links between EMF and cancer or diseases
such as Alzheimer’s However, there is little or no
conclusive evidence that the level of EMF currently
experienced by the general population does cause
ill health, but on the basis of current scientific
knowledge the question of whether the use of
mobile phones poses an increased risk of cancer
is still an open question
Novel electrical and electronic technologies,
new communication devices, magnetic imaging
technologies for medical use and other applications
bring new EMF challenges that must be assessed
for risk
organisms in FP5 Legislators need validated scientific evidence to establish the safety standards and exposure limits, while manufacturers need
to have guidelines for safe product design The environment and health projects funded in FP5 have contributed to this vital research effortProjects in this area represent around 9% of the total budget for environment and health in FP5
Terahertz Radiation and Health – 2 projectsThe majority of the projects looked at radiofrequency fields and health due to the increased concern from the widespread use of
2
The electromagnetic spectrum includes X-rays, sunlight, visible light, infrared, microwaves, radio waves and at low
frequency radiation from power lines and other electric fields The energy of electromagnetic radiation is proportional
to frequency, so X-rays with high frequency are very energetic and are known as ionising radiation as they can break
chemical bonds and produce charged atoms called ions
Lower energy, or lower frequency, electromagnetic radiation – to the left of the visible region - is non-ionising as it
cannot break chemical bonds, but it can interact with matter in other ways This is the source of potential risk from EMF
that is of interest to researchers in this context
Trang 30GSM/mobile phones in society Although final
reports are still due for some projects, there
is a reasonable consensus that no significant
observable adverse effects have been discovered
relating to GSM use, although further work will be
required to investigate detailed responses
However, some adverse genotoxic interactions
of EMF of the type generated by 50 Hz mains
electricity were observed in a particularly sensitive
set of tests
Terahertz radiation is used in medical applications
and is often found at exits to shops, for example,
to detect and deter shoplifting The results from the
FP5 research projects showed that such devices
induce no adverse effects under the experimental
conditions employed A number of recommendations
for improvements to the exposure guidelines for
terahertz security devices were made
Further work
Within FP6 the work on EMF was specifically
continued in the coordination action EMF-NET20
(Effects of the exposure to Electromagnetic fields:
From science to public health and safer workplaces),
which is working to bring together research results
on biological effects of EMF including occupational
exposure A COST21 action was also funded, focused
on health risks related to emerging technologies
The Environment and Health activity within the
Environment (including Climate Change) theme
of the Cooperation Programme in FP722 includes
specific reference to health effects of EMF and
other funding may be possible under calls from the
Information and Communication Technologies and
Health themes
FP5 projects list
Brief details of each project in this area are given
below For more details please see the individual
project summary sheets
Radiofrequency Fields and Health
CEMFEC –Combined effects if Electromagnetic Fields with Environmental Carcinogens
At the levels of exposure chosen no carcinogenic effects due to radiofrequency exposure were found
GUARD – Potential Adverse Effects of GSM Cellular Phones on Hearing
No effects due to GSM phones on the main measures of auditory status in animals or humans could be found, but study of potential effects in the auditory efferent system were recommended
[Page 168]
INTERPHONE –International Case Control Studies
of Cancer in Relation to Mobile Phone Use This project is aiming to give a definitive answer to the question: “do mobile phones increase cancer risk” through a wide-ranging, multi-country study
on the occurrence of tumours in cells in close proximity to phones during use such as the brain, acoustic nerve and parotid gland The final report is
RAMP 2001 – Risk Assessment for Exposure
of Nervous System Cells to Mobile Telephone
EMF: from In Vitro to In Vivo Studies
No specific effects were found in this in vivo and in vitro study of the possible effects of electromagnetic
fields on the brain and nervous system [Page 172]
PERFORM-A – In vivo Research on Possible Health Effects related to Mobile Telephones and Base Stations (Carcinogenicity Studies in Rodents)
Six animal models are being used to determine
if radiofrequency exposure induces or promotes cancer in mice and rats The final report is due
Trang 31Environmental Hazards from Low-energy
Electromagnetic Field (EMF) Exposure using
Sensitive in vitro Methods
Intermittent exposure to 50 Hz low-frequency
electromagnetic fields, such as that generated by
mains electrical installations in Europe, was shown
to have genotoxic effects on human fibroblasts,
melanocytes and some animal cells [Page 176]
Terahertz Radiation and Health
ADVICE PULSED FIELDS – Health Impact
from the Use of Security and Similar
Devices Employing Pulsed and Continuous
Electromagnetic Fields
Security devices, such as those often found at the
exit of stores, use EMF and although exposure
of citizens and workers generally did not exceed
international limits this study recommended a
number of proposals for improvement – the ultimate
aim would be complete compatibility between
medical and security devices [Page 178]
THZ-BRIDGE –Tera-hertz radiation in Biological
Research, Investigations on Diagnostics and
Study on Potential Genotoxic Effects
The study found that use of tera-hertz radiation in
medical applications using appropriate limits should
not cause harm to subjects - at least for a single
31
Trang 32Noise-related
health impacts
Noise annoys Europe
In Europe it is estimated that:
113 million people are exposed to noise levels high enough to have serious health consequences
10 million people are exposed to ambient noise levels that can lead to hearing loss
30 million people are exposed to occupational noise that endangers their hearing
European context
As can be seen from the figures (see box) noise is
the environmental factor that reaches, and disturbs,
the largest number of Europeans We live in a world
of noise; in fact many city dwellers feel distinctly
uncomfortable in remote rural places where the
constant urban rumble is silent!
Noise can interfere with communication, cause
sleep disturbance and cardiovascular effects
It can affect metal health, reduce performance,
causes annoyance and can alter social behaviour
At high levels it can impair hearing There are also
suggested links to children’s ability to learn The
greatest disturbance at the social level is created by
transport, whilst the greatest hazard is probably still
to be found in heavy industry
FP5 projects –
Highlighting noise as a problem
It is hard to estimate the exact impact of noise itself
as it is often accompanied by other environmental
hazards such as air pollution or chemical
exposure Research under FP5 has drawn
attention to noise-related health effects and is
providing scientific evidence for establishing clear
noise regulation in the European Union The four
research projects explicitly on noise represented
just over 4% of the budget allocated under FP5
environment and health
Research results
Three of the FP5 projects related primarily to transport noise Clear evidence of links between noise effects and classroom performance and a number of health indicators were made, although some conflicting evidence was observed between different transport modes The additive effect of noise on top of other environmental stressors, for example chemical solvents, was also clearly demonstrated
In addition to these results, aspects of noise pollution health effects were also investigated in the wide ranging PINCHE project and the HEARTS projects on health effects of transport (the additive effect of noise with other stressors) The PINCHE network made a specific recommendation to limit noise exposure from personal music players, such as MP3 players, to young people For more information on both these projects see the Multiple Stressors chapter
The mounting evidence from FP5 and previous research was a significant input to the EU Directive
on Environmental Noise adopted in June 2002 that laid down a common basis for tackling noise problems across Europe
Further work
In FP6 no specific projects on noise and health were funded, but noise was included as an important environmental stressor in major integrated
32
Trang 33assessment projects such INTARESE23 Other FP6
projects which cover aspects of noise pollution in
their remit, but are not directly health-related, are
HARMONOISE24 (New methods for noise mapping),
IMAGINE25 (Improved methods for the assessment
of the generic impact of noise in the environment)
and CALM26 (Coordination of European research for
advanced transport noise mitigation)
For FP7 noise is included as one of the priorities
for funding within the Environment and Health
activity 1 “Health effects of exposure to emerging
environmental stressors” within the Environment
(including Climate Change) theme of the Cooperation
programme27
project summary sheets
Noise and Health HYENA –Hypertension and Exposure to Noise near Airports
This study evaluated impacts of aircraft and other transport noise on the blood pressure of local residents, the effects of traffic-related pollution and stress-related hormones Its final report is due
NOISECHEM – Noise and Industrial Chemicals:
Interaction Effects on Hearing and Balance
The combination of noise and organic solvent exposure in the workplace leads to higher than expected hearing loss This multiplying effect means Occupational Exposure Limits for solvents may not sufficiently protect exposed workforces [Page 184]
NOPHER – Noise Pollution Health Effects
Reduction
This project has brought improved focus to research
on noise pollution and health in Europe and developed a consensus on the strength of causal relationship between noise and health effects
[Page 186]
RANCH – Road Traffic and Aircraft Noise Exposure and Children’s Cognition and Health: Exposure-effect Relationships and Combined Effects
High levels of aircraft noise can impair a child’s reading ability, but this effect is not reflected in observations made on road traffic No relationship between noise and health was found and links between noise and blood pressure and sleep disturbance were inconclusive [Page 188]
Trang 34UV light and ionising related health impacts
radiation-The ABC of UV
Ultraviolet (UV) light is part of the electromagnetic spectrum It is found at frequencies higher than visible light and is therefore invisible to the human eye – although some animals can see in UV It is more energetic than visible light When considering the effect of UV radiation and the environment the UV range is often subdivided into UV-A, UV-B, UV-C The energy of the light increases from A to C Fortunately most UV-B and UV-C is filtered out by the atmospheric ozone layer found at high altitude as this has greater ionising potential – the ability to break chemical bonds and produced charged molecules and atoms called ions
European context
A lazy day in the sun is enjoyable for most people
Most of us imagine sunny days on the beach or
in the countryside when we think about vacations
Exposure to UV-B light also induces the production
of vitamin-D Lack of vitamin D can lead to a range of
cancers and also bone disease Ultraviolet radiation
is used in medical applications for the treatment of
some skin conditions such as psoriasis
However, UV light has the capacity to break chemical
bonds and targets multiple molecules in living tissue,
including DNA It can be harmful to the eyes, skin and immune system and is a major and increasing cause of skin cancer UV can also react with a diverse range of chemicals, due to its bond breaking ability, turning benign species into harmful carcinogens
FP5 projects – UV light and cancer
The research aimed to identify carcinogenic environmental factors due to UV, explain how the effects are expressed and detect early signs of harmful exposure and oxidative stress This can lead to new strategies for countering carcinogenic
processes before they lead to cancer itself
Other health and safety aspects
of ionising radiation sources, such as those found in medical applications (X-rays), are covered mainly under European research carried out for the Euratom Research Framework Programmes
Five projects were undertaken
in this area during FP5 They represent around 4% of the total budget allocated under environment and health
34
Trang 35was highlighted in melanoma development and two
genetic biomarkers that could help early diagnosis
of a health issue due to UV-A stress were identified
Studies also indicated that prophylactic medical UV
should not be used to prevent UV induced immune
health risks A large-scale investigation of sun allergies
showed their prevalence in Europe and illuminated
some new therapies and medical guidelines
Another aspect of ionising radiation is the long-term
effect of large scale nuclear accidents on health A
review of the effect of post event iodine medication
on thyroid cancer following the Chernobyl incident
demonstrated that this was a useful precaution if
similar events took place in the future
Future work
No specific projects on UV radiation health effects
were undertaken in FP6 but they were included
in the multiple stressor risk assessment projects
such as INTARESE and NOMIRACLE In FP7 UV
will be one of the environmental stressors evaluated
as part of the integrated approaches under the
Environment theme of the Cooperation Programme,
Environment and Health activity.28
FP5 Projects list
Brief details of each project in this area are given
below For more details please see the individual
project summary sheets
IHA-UV –Immunological Health and Adaptation
following Chronic Exposure to Environmental
Ultraviolet (UV) Radiation
By monitoring skin adaptations during UV radiation
courses on both human and animal subjects it
was concluded that, overall, the use of low-dose
UV exposures as a precautionary measure to
reduce UV induced immune health risks could not
Damage to a single tumour suppressor gene was shown to play a key role in melanoma development The role played by heat and UV-A radiation was also highlighted in the formation of malignant tumours
[Page 192]
PREVENTION BIOMARKERS – New markers of Oxidative Stress to Humans: a Role in Developing New Strategies for Human Protection against Environmental (UV-A) Damage to Skin
Bio-New biomarkers for environmental stress due to
UV-A exposure were developed and tested Two genes known to be activated by oxidative stress were shown to be consistently activated by UV-A stress
on the skin of people on a low flavonoid diet
[Page 194]
SUNALL –Allergy to the Sun: Multidisciplinary Investigation on the Pathogenesis, Treatment and Prevention of Polymorphic Light Eruption across Europe
Polymorphic Light eruption is one of the more common sun-provoked skin allergies This project sought to determine the prevalence and severity of the condition across Europe improving diagnostic criteria, targeting new therapies and providing guidelines on prevention Final report will be
THYRRISK – Environmental and Host Factors in the Risk of Thyroid Cancer
This project will recommend the preventative ingestion of iodine following exposure to radioactive iodine to reduce thyroid cancer risk The result derives from a large case-control study on thyroid cancer risk in the Belarus and Russia post Chernobyl
[Page 198]
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28 http://cordis.europa.eu/fp7/home_en.html
Trang 36Multiple stressors and factors and health impacts
European context
Exposure to only a single environmental stressor in
normal life is unlikely What is the cumulative effect of
the variety of environmental stressors that we face
as part of daily life? Is the effect additive, negative,
zero or more complex? Clearly there is a need to
understand the interactions of stressors and adapt
regulation and risk management accordingly
FP5 projects and Research results –
Reflecting complexity
A small number of diverse projects were launched
in FP5 to assess and attempt to unravel the relative
contributions of multiple environmental stressors to
certain health issues
The seven projects undertaken in this area
represent over 5% of the FP5 budget allocated
to environment and health Their diversity means
that broad analysis of the results is not feasible
However, the methodology employed – integrated
environment and health risk assessment – showed
its effectiveness and utility and pointed the way
forward for future FPs
Integrated risk assessment projects obtained over
30% of the funding during FP6 and this approach
of integrating multiple factors to obtain a more
“real-world” picture will continue in FP7
FP5 Projects list
Brief details of each project in this area are given
below For more details please see the individual
project summary sheets
E21-4AYC – Environmental Influences and Infection as Aetiological Agencies in Atopy and Asthma in Young Children
Important gene-environment interactions in the development of atopy and asthma were found and suggest that reducing domestic allergen exposure alone will not decrease disease incidence However, indoor NO2 was clearly associated with lower respiratory tract infection The study results do not support delayed introduction of solid food as protective in development of asthma and allergy
to sunlight during childhood Decreased risk was observed for subjects with diabetes, hypertension, asthma, arthrosis and a history of food allergy Regular statin (cholesterol lowering medication) use also reduces lymphoma risk [Page 202]
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Trang 37effects of road transport incorporating noise,
emissions, road crashes, air pollution, pedestrians
and exposure modelling was developed New
approaches to urban planning will be required with
investment to reduce traffic emissions and improve
indoor air quality in public transport [Page 206]
PARSIFAL – Prevention of Allergy – Risk Factors
for Sensitisation in Children related to Farming
and Anthroposophic Lifestyle
Farmers’ children and Steiner school children were
both found to exhibit lower markers for atopic
disease than their control groups This protective
effect was broadly applicable House dust samples
suggest the children are exposed to higher levels
of endotoxin, exopolysaccharides and glucans than
the controls; differences in intestinal bacteria have
PASTURE – Protection against Allergy: Study in
Rural Environments
Comparisons of farming and non-farming families
showed differences in serum IgE levels between
farming and non-farming newborns and differing
maternal exposures were reflected in cytokine levels
PDCAAE – Prevalence and Determinants of
Childhood Asthma and Allergies across Europe
The study found that links between asthma and
atopic sensitisation differ between populations
and economic development factors are important
mediators Risk factors include lifestyle and
environmental factors with a substantial underlying
heterogeneity of genetic risk factors for asthma
[Page 212]
PINCHE – Policy Interpretation Network on
Children’s Health and Environment
Recommendations to protect childrens’ health and
environment include, in priority order: reducing
exposure to traffic pollution, environmental tobacco smoke, allergic symptoms, ozone, hydrocarbons, metals such as arsenic, lead, cadmium and mercury, and reducing a variety of indoor pollutants such
as mould, radon and formaldehyde Detrimental, excessive exposure to noise from personal music players was also highlighted as a hazard
[Page 214]
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Trang 38Waterborne stressor-related
health impacts
European context
The provision of clean drinking water has a key role
in establishing public health: maintaining the quality
of all water used for bathing is also essential
Waterborne pathogens, other bacteria and
contamination (including arsenic and cadmium)
are easily assimilated into the body and can have
severe health effects
FP5 projects and Research results –
Safer water
Around 3% of the total FP5 funding allocated under
environment and health was spent in this area Work
included new DNA chip technology for water quality
assessment that should help ensure the safety of
bathing and drinking water across Europe New
methodology and better understanding was also
developed for cyanotoxin risk assessment studies
that will reinforce public health protection in line with
WHO and EU directives The dental community and
their patients will benefit from the results of a risk
assessment of water quality in dental units – this
identified a need for cleaning products that target
biofilm formation
Future work
In FP6 four further projects representing 6% of
the budget under Environment and Health were
undertaken on waterborne stressors These
ongoing projects cover assessment of human
health effects caused by bathing waters
(EPI-BATHE29), assessment of human health impacts
from emerging microbial pathogens in drinking
water by molecular and epidemiological studies (HEALTHY WATER30), methods for detection of viruses in bathing water (VIRO-BATHE31) and health impacts of long-term exposure to disinfection by-products in drinking water (HI-WATE32)
For FP7 research on waterborne stressors is included as one of the priorities for funding within the Environment and Health activity 1 “Health effects
of exposure to emerging environmental stressors” within the Environment (including Climate Change) theme of the Cooperation programme33
FP5 Project list
Brief details of each project in this area are given below For more details please see the individual project summary sheets
Waterborne Stressors and Health
AQUACHIP –Development and Validation of a DNA-Chip Technology for the assessment of the Bacteriological Quality of Bathing and Drinking Water
The DNA chip technology successfully developed was able to show that drinking and bathing water samples all displayed habitat-specific molecular fingerprints of bacterial microflora with seasonal variations: these fingerprints could act as quality
Trang 3944% of the dental water samples analysed failed
to meet current EU potable water guidelines with
biofilms identified as the main source of bacterial
contamination and should be targeted Other
pathogens detected indicate potential for cross
PEPCY – Toxic and Bioactive Peptides in
Cyanobacteria
The central objective was to improve cyanotoxin
risk assessment and management and a risk-based
and setting-specific methodology to public health
protection from cyonotoxins was developed in line
with WHO drinking water quality and EU Bathing
Water Directive approaches [Page 220]
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Trang 40Climate change-related
health impacts
European context
The effect of climate change on the environment
is yet another complicating factor to add into
a complex situation Modelling of the effects of
global warming indicate a substantial increase in
average temperatures for Europe over the next
decades, possible rises in sea level and a greater
frequency of extreme weather events These
in themselves will impact on health But these
changes in the environment will also affect the
geographical distribution of disease, pathogens
and other undesirable organisms with additional
human health impacts
FP5 Actions and Research results – Additional stress
Only two projects were funded: one looked to model the potential effects of global warming on human diseases patterns and possible adaptation strategies, the other examined acute health effects Both showed that climate change would exacerbate existing or add new environmental stressors to the health issue The funding represented less than 2%
of the total allocated under Environment and Health
of one of the main themes: Environment (including climate change) and research on health impacts of climate change will
be funded from the Environment and Health activity36
FP5 Project list
Brief details of each project in this area are given on the next page For more details please see the individual project summary sheets
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34 http://www.eden-fp6project.net/
35 Website under construction
36 http://cordis.europa.eu/fp7/home_en.html