Despite improvements in air quality over the last few
decades, air pollution continues to seriously affect people's
health. A study in the Bristol area argues that further research
is needed to measure the long-term impacts
Since the 1950s, a significant body of evidence has accumulated
showing that air pollution has a damaging effect on health and is
associated with increases in outpatient visits due to respiratory
and cardiovascular diseases, in hospital admissions and in daily
mortality.1
Ozone is a powerful oxidant which causes inflammation of the respiratory
tract and exacerbates existing lung disease. Particulates, particularly
fine particles of diameter less than 10µ (PM10) which can
penetrate deep into the lungs, are linked with heart and lung disease.
Volatile organic compounds (VOCs) (such as benzene and 1,3-butadiene)
originate predominantly from traffic exhausts and many are carcinogenic,
irritant or toxic, although this is dependent on the specific compound.
In the UK, only benzene and 1,3-butadiene are currently classified
as particularly harmful in the National Air Quality Strategy (NAQS)
because of their status as carcinogens.2
Although most data on the toxicity of VOCs stems from very high
dose studies, low background levels may still affect human health.
Studies of indoor air pollution and "sick building syndrome"
have found connections between the mixtures of VOCs present in these
environments and adverse health effects such as headaches and sensory
irritation.3 It should be noted
that many compounds classed as pollutants do occur naturally in
the atmosphere and our cardio-respiratory systems have evolved to
cope with these background levels. However, any chemical whose level
is elevated above normal may be implicated in causing an adverse
health effect.
The complex mix of chemicals present in urban air makes it difficult
to attribute specific health effects to any one compound and they
may stem from cumulative or synergistic effects.4
It is possible that the cocktail of VOCs present in the urban atmosphere
may be adding to the health impact of the criteria pollutants such
as ozone and PM10, hence the inclusion of benzene, 1,3-butadiene
and total volatile organic compound concentration (TVOC) in this
study.
Air pollution and health
Studies of air pollution and health in the UK have mostly focused
on London, although some have also been carried out in other large
cities such as Birmingham and Edinburgh. The main associations found
have been between particulate matter and all-cause mortality, including
specific cardiovascular and respiratory mortality. The APHEA project
(Air pollution and health: a European approach) has attempted to
provide quantitative estimates of the acute effects of air pollution
on health in 11 cities across Europe.
The study found that particulates, sulphur dioxide, nitrogen dioxide
and ozone were all associated with increased all-cause or cause-specific
mortality to a greater or lesser extent.5
A report commissioned by the Department of Health and produced by
the Committee on the Medical Effects of Air Pollutants (COMEAP)
estimated that PM10 and SO2 were responsible for the advancement
of over 11,000 deaths in Great Britain every year.6
Despite the large number of studies that have been carried out
over the years it is hard to find repeatable results which can be
automatically applied to many situations. Even in the same country,
no cities have exactly the same pollutant composition or population
with respect to age distribution, social status, underlying health
and exposure to other risks such as climate or weather. It is therefore
difficult to extrapolate findings from a study in one area to a
different place. A study using data from Bristol must be undertaken
to ascertain whether current levels of air pollution are having
a significant effect on the population of the city.
In Bristol, Sarah McMahon and colleagues working at the University
of the West of England (UWE) and Bristol City Council have undertaken
several projects to quantify the effects of air pollution in Bristol
on the local population. The first study examined the effect of
particulate concentrations on emergency hospital admission for respiratory
disease between December 1992 and June 1993.7
Positive correlations were found in both the summer and winter.
Further studies specifically investigated the effects on children
of primary school age who suffered from asthma. The use of ventolin
inhalers (those used for the relief of symptoms) was found to be
associated with fine particles and NO2. These effects were seen
in children across the region, responding to the same high pollution
episodes whose effects could be felt across the entire study area.8,9
Analysing data
The Avon Health Authority (AHA) provided information on daily cardiovascular
mortality, respiratory mortality, all cause mortality and population
in the Bristol area (BS1 to BS40 inclusive) for the period of January
1996 to December 1999. Causes of death were classified according
to the International Classification of Diseases (Revision 9). Circulatory
and cardiovascular diseases are classified as ICD-9 codes 390-459
and respiratory diseases as 460-519. The data was broken down into
four age groups: under 17, 17-44, 45-64 and over 65. Pollution data
was obtained from the National Air Quality Information Archive for
the two continuous air quality monitors in the city centre which
are part of the National Automatic Monitoring Network and operated
by the National Environmental Technology Centre (NETCEN). Weather
data was provided by the British Atmospheric Data Centre for a weather
station located in central Bristol.
The STATA statistics package was used to analyse the data set
with a multiple linear regression model. A multi-factor analysis
can begin to account for confounding issues, such as the fact that
all of the pollutants correlate with each other and with the weather,
as well as potentially with the health outcomes. The daily health
outcome data was compared with daily average levels of ozone, PM10,
benzene, 1,3-butadiene and TVOC. Confounding by weather was accounted
for by the inclusion of average daily temperature and wind speed
in the model. Lags of up to five days were applied to the data and
the results were tested at the 95 per cent confidence level.
Statistical correlations
A number of statistically significant correlations were found in
the data for Bristol. The associations were generally found in the
oldest age group (over 65).
Weather: temperature showed a consistently strong negative
correlation with mortality, especially in the older age groups (ages
45-65 and over 65). Wind speed exhibited no significant correlations.
The medical and epidemiological community has long known of the
link between weather and adverse health outcomes. In this country,
the greatest effect of temperature is during winter when the number
of cases of influenza and other diseases of the respiratory system
rise. The spread of these infectious illnesses is exacerbated during
colder weather. It is encouraging that this expected result was
consistently found in the analyses, as it demonstrates that effects
can be observed in the data using this statistical method.
Particulate matter: levels of PM10 were consistently associated
with increases in all-cause and cause specific mortality in the
over 65 age group. These connections were found for each lag period,
although the strongest association was on the same day. The effect
was strongest for cardiovascular deaths, less strong for respiratory
deaths, and somewhere in between for all-cause mortality. A similar
order of effect for PM10 was also found in the APHEA study of Western
European cities.5 A quantifiable
effect of PM10 on respiratory disease in Bristol was also found
by McMahon,7 albeit in daily admissions,
but it would be expected that incidences of admissions and mortality
are closely linked.
Ozone: ozone showed a positive correlation with cardiovascular
mortality in the over 65 age group for a one-day lag. Ozone has
found to be associated specifically with cardiovascular disease
in several other UK studies as well as in the APHEA project. 10,11,5
In the APHEA project however, ozone was more strongly correlated
with all cause and respiratory mortality, effects which were not
found in this analysis.
TVOC: concentrations of TVOC showed a positive association
with next-day respiratory deaths in the over 65 age group. Very
few studies of outdoor air pollution have investigated the influence
of VOCs on health but those that have done so have found VOC concentrations
to be associated with respiratory illnesses. One study of school
children in West Virginia found a positive correlation between chronic
respiratory symptoms and VOC concentrations.12
A study at a London accident and emergency department found that
levels of benzene, propane and isoprene had a significant positive
linear relationship with attendances of very young children for
acute wheeze.13 In a Norwegian
study benzene was found to be more strongly associated with emergency
hospital admissions for respiratory disease than PM10.14 In the
Bristol data the correlation coefficients for TVOC were very similar
to those for PM10, suggesting a similar magnitude of effect.
Limitations of methods
The limitations of the methods used in this study must be borne
in mind when deciding on the significance of the results. It must
be remembered that the numbers of deaths and hospital admissions
that are being dealt with are very low. The average number of deaths
(from all causes) in the Bristol area is 23 a day, in a total population
of almost 900,000. Around 45 per cent of these deaths are from cardiovascular
disease and 15 per cent from respiratory illness.
Identifying and quantifying small fluctuations in a low number
of incidences is inevitably hard. The statistical method used -
multiple linear regression - assumes that the relationship between
the variables is linear. The complex interplay of pollutants and
weather means this is not always the case. Other factors which must
be considered include the spatial variation of pollutant concentrations
across a large region and confounding issues such as bed availability.
Nevertheless, this analysis has produced similar results to those
found by more complex investigations.
Levels of pollutants in the Bristol area are not generally considered
dangerous to human health according to current government standards.
The Government's air quality index is used to describe the severity
of air pollution using a banding system.2
During the entire period of this study, air pollution in Bristol
was generally "low" and occasionally "moderate",
never "high" or "very high" according to the
index. Despite this, an association has still been identified between
daily concentrations of pollutants, notably PM10, and mortality.
These effects were overwhelmingly seen in people aged over 65.
This is unsurprising, given the increased vulnerability of this
age group. Cold weather and "flu" epidemics are known
to hasten mortality in the sick and elderly and the COMEAP report
concluded that it was likely that air pollutants could act in a
similar manner, bringing forward death by a few weeks or days.6
If air pollution is advancing mortality then it could also be
expected that it is adversely affecting hospital admissions, attendances
at hospitals and doctors surgeries and the occurrence of symptoms
of respiratory or cardiovascular disease. Further research could
elucidate the effect of air pollution on the quality of life of
the wider population and its impact on economic factors such as
numbers of sick days or early retirements. The chronic, long-term
impact of poor air quality on human health is a subject which is
only just beginning to be explored. This is potentially more important
in public health terms than the acute (short-term) effects. Two
American studies have indicated that life expectancy may be two
or three years shorter in communities with high particulate levels
compared with those communities which experience lower levels.15,16
The linear regression models used in this study have identified
an association between daily levels of pollutants (particularly
PM10) and increased mortality in the Bristol area. These findings
are in keeping with the results of similar studies from other cities
in the UK and indicate that further investigation into the acute
and chronic effects of poor air quality is warranted.
Alison Rivett, Dudley Shallcross and Ruth Wood, are from the
School of Chemistry at University of Bristol, and Ben Wheeler and
David Gunnell are from the Department of Social Medicine. For further
details contact Alison Rivett by e-mail: a.c.rivett@bristol.ac.uk
Thanks to Sarah McMahon at Bristol City Council for many useful
discussions and information on this topic. Thanks also to David
Prothero and Angela Chung at the Avon Health Authority for making
available the health data.
References
WHO (2000). "Guidelines for air quality", World Health
Organisation, Geneva.
COMEAP (1998). Quantification of the effects of air pollution
on health in the United Kingdom. Committee on the Medical Effects
of Air Pollution, Department of Health, London.
McMahon S K, (1993). Particulate air pollution and respiratory
health in Bristol. MSc Thesis, University of the West of England,
Bristol.
McMahon S K, Fryer P, (1995). "Asthma in Children".
Environmental Health Journal, July, 161-162.
McMahon S K, (2001). "Accelerating the symptoms: A study
of traffic pollution and respiratory health of primary school
children living in the Bristol area". Environmental Health
Journal, June, 176-178.
Anderson H R, de Leon A P, Bland J M, Bower JS, Strachan DP,
(1996). "Air pollution and daily mortality in London":
1987-92. British Medical Journal, 312, 665-669.
Bremner S A, Anderson H R, Atkinson R W, McMichael A J, Strachan
D P, Bland J M, Bower J S, (1999). "Short-term associations
between outdoor air pollution and mortality in London 1992-4".
Occupational Environmental Medicine, 56, 237-244.
Ware J H, Spengler J D, Neas L M, Samet J M, Wagner G R, Coultas
D, Ozkaynak H, Schwab M, (1993). "Respiratory and irritant
health-effects of ambient volatile compounds - the Kanawha County
health study". American Journal of Epidemiology, 137, 1287-1301.
Buchdahl R, Willems C D, Vander M, Babiker A, (2000). "Associations
between ambient ozone, hydrocarbons and childhood wheezy episodes:
a prospective observational study in south east London".
Occupational Environmental Medicine, 57, 86-93.
Hagen J A, Nafstad P, Skrondal A, Bjorkly S, Magnus P, (2000)."
Associations between outdoor air pollutants and hospitalisation
for respiratory diseases". Epidemiology, 11, 136-140.
Dockery D W, Pope C A III, Xu X P, Spengler J D, Ware J H,
Fay M E, Ferris B G, Speizer F E, (1993). "An association
between air pollution and mortality in six United States cities".
New England Journal of Medicine, 329, 1753-1759.
Pope C A III, Thun M J, Namboodiri M M, Dockery D W, Evans
J S, Speizer F E, Heath C W, (1995). "Particulate air-pollution
as a predictor of mortality in a prospective-study of US adults".
American Journal of Respiratory and Critical Care Medicine, 151,
669-674.