![]()
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
How important is urban air pollution as a health
hazard?
Simon Kingham
I am writing this editorial from Ashburton having been
displaced from my badly damaged house in Christchurch following the earthquake
of 22 Feb 2011. It is with great sadness that we are now counting the loss of
life with upwards of 200 people thought to have died and a reconstruction bill
that will run into the billions. In comparison, air pollution in New Zealand is
estimated to result in about 1100 deaths per year and cost over $1 billion in
health-related costs.1 These impacts of these
two hazards are in many ways quite different.
Natural disaster-related hazards such as flooding, tsunamis
and earthquakes have very visible impacts. The physical environment is
demonstrably changed and the dead and injured can be seen and identified. The
impacts of air pollution are usually quite different however. In developed
countries today we rarely get short high-pollution events like those experienced
in Meuse Valley in 1930, Donora in 1948, and London in 1952. Instead we get
lower levels of pollution which we know have the potential to harm health.
However, this means that illness and death is not immediate and not always
easily attributable to specific temporal event. This fact makes the science
highly contested, and is the basis for three of the papers in this issue of the
Journal.2–4
The three Christchurch-based authors; John Hoare, Pat
Palmer, and Peter Moller; are all members of the Association for Independent
Research (AIR). All three, in different ways, question the effect wood smoke
from domestic home heating has on health, without presenting any new primary
data.
Palmer bases his assertion on the fact that the
dose-response relationships appears much stronger in summer (when there is
little or no wood smoke) than winter, and he concludes that wood smoke
“despite its predominance as a component in the winter PM10 may be
relatively harmless”.
Hoare suggests that the small dose-response relationship
coupled with the range of other confounding factors may be leading to spurious
findings, and finally Moller suggest that the 24-hour standard is inappropriate
for the low levels of pollution experienced and asserts that the impacts on the
ability of socioeconomic groups to heat their homes if wood use is restricted
are worthy of consideration.
This goes against the broad belief that particles, whatever
the source and even at low levels, are damaging to health. This is enshrined in
guidelines and standards throughout the world—including the World Health
Organization (WHO), the European Union, the US Environmental Protection Agency,
and the New Zealand Government—which do not differentiate between the
source of particles.
In relation to PM2.5 the WHO states:
...although few epidemiological studies have compared
the relative toxicity of the products of fossil fuel and biomass combustion,
similar effect estimates are found for a wide range of cities in both developed
and developing countries. It is, therefore, reasonable to assume that the health
effects of PM2.5 from both of these sources are broadly the
same.5
Recent research has started to examine the issue of toxicity
of different source particles and the findings are inconclusive with some
suggesting that biomass/wood smoke does have an
effect6 while others such as Clark et
al7 have not identified a relationship.
More locally, another study in New Zealand has suggested
that there is a possibility that vehicle emissions may have a lesser impact on
health than wood smoke.8 This is clearly an
area where further research is needed, but until is clearly demonstrated that
wood smoke does not effect health, then it would seem prudent to err on the side
of caution and retain the current air quality standards that assume it does.
Current air quality standards and guidelines are limited in
that they are based on a pollution value being exceeded at a fixed ambient site.
In addition the vast majority of research both internationally and in New
Zealand has generally used measures of pollution exposure that lack either
spatial or temporal accuracy.9 Yet is widely
accepted that the quality of, and/or lack of, exposure data are often a weakness
in studies examining links between air quality and health.
Two papers10,11 in this
issue of the Journal by Nick Wilson et al attempt in a small way to
address this issue; one looking at secondhand smoke in public spaces and the
other at air pollution in takeaway outlets and 'barbecue' restaurants. In both
cases very high short-term exposures to particulate matter were recorded. These
types of exposures, along with other more frequent ones such as while travelling
along roads, are not covered by air quality standards. In addition they are
rarely captured in research that compares ambient pollution levels and health.
Yet there is evidence that for some people time spent in these environments that
can be a significant part of their daily exposure.
Pollution exposure in micro environments is something that
clearly needs more attention in studies that examine the impact of the quality
of the air we breathe on our health.
Competing interests: None.
Author
information: Simon Kingham, Head of the Department of Geography and
Co-Director of the GeoHealth Laboratory, University of Canterbury (Te Whare
Wananga O Waitaha), Christchurch
Correspondence: Associate Professor Simon Kingham, Department of Geography, University of Canterbury, Private Bag, Christchurch, New Zealand. Fax: +64 (0)3 3642907; email: simon.kingham@canterbury.ac.nz References
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Current
issue | Search journal |
Archived issues | Classifieds
| Hotline (free ads) Subscribe | Contribute | Advertise | Contact Us | Copyright | Other Journals |