The indoor environment and the lung. 96/4
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Most people in Britain spend over three-quarters of their time
indoors and personal exposure to many air pollutants is thus determined
more by concentrations indoors than outdoors. Whereas air pollution
outdoors is routinely monitored from fixed sites, much less is
known about the levels of air pollution indoors. This is because
indoor air quality may vary a great deal from one building to
another, depending upon the rate of emission from the structural
components, internal fittings and heating devices, the rate of
natural and artificial ventilation and, for many pollutants, the
activities of the occupants. Relationships between the indoor
environment and respiratory health have recently been reviewed
with a view to revising building regulations and setting guidelines
for indoor air quality (see footnote). This factsheet summarises
the sourced and possible health effects of indoor pollutants which
are known or suspected causes of respiratory disease.
Figure 1: Sources of indoor pollutants
The components of indoor air primary concern with respect to lung
disease may be grouped as irritants, allergens or carcinogens.
This list excludes microbial pathogens, although some of these,
such as Legionella pneumophila, may be related to the building
design.
Figure 2:Sources of indoor pollutants
The main source of indoor pollutants within the home are illustrated
in here. However, the presence of an emission source is not always
a good predictor of indoor pollutant levels, which depend also
on the rate of removal by ventilation or absorption, and the pollutant
concentration in outdoor air. For particulate matter such as allergens,
the airborne concentration also depends on dispersal by activity
patterns within the room
Figure 3:Health effects of indoor pollutants
This summarises the principal known or suspected respiratory
effects of indoor air pollutants. The evidence linking specific
pollutants to ill-health is often incomplete, and is rarely sufficient
to quantify the effect of different levels of exposure on the
occurrences of disease (dose-response relationship). For some
contaminants such as radon and asbestos, occupational exposures
at high levels provide strong evidence of cancer risk, although
uncertainty arises in extrapolating to the lower levels of exposure
typically encountered in homes. For others, such as nitrogen dioxide,
domestic exposure provides the clearest evidence of an association
with disease, but the levels which are generally lower than those
causing adverse effects in experimental exposure studies. A third
group are those pollutants for which toxicological experiments
or anecdotal case-reports suggest a health hazard but there is
insufficient or inconsistent epidemiological evidence to confirm
or exclude an effect of importance to public health.
Radon is the only pollutant for which specific indoor air quality
standards have been set in the United Kingdom. Above an "action
level" of 200 Bq/m³ for existing homes, home owners
are urged to take measures to reduce radon concentrations. An
estimated 100,000 of the 21 million homes nationwide are above
this action level.
Summary
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Many irritants, allergens and carcinogens may be present
in indoor air.
-
Pollutant concentrations are often higher indoors than outdoors,
but the levels of exposure encountered in typical British
homes are not routinely monitored.
-
Respiratory health effects of many indoor pollutants are
known or suspected, but the "dose-response" relationship
between level of exposure and risk of disease is poorly understood,
and the effects of reducing exposure cannot be predicted with
certainty.
-
Indoor air quality guidelines do not exist for most domestic
pollutants, although action levels have been set for radon.
Footnote
The evidence summarised here is discussed at greater length in
two publications:
Raw GJ.Hamilton. Building regulation and health. Watford, Building
Research Establishment, 1995
Humfry C Shuker L, Harrison P. Indoor air quality in the home.
Leicester, Institute for Environment & Health, 1996
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