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bushfire Smoke research
The composition and quantity of smoke burning during the dry season in northern
produced during a fire will differ depending Australia caused an increase in hospital visits Other CRC projects are researching aspects of
on the chemistry and condition of the for asthma (1) but the same effects were not bushfire smoke.
fuel, the amount and arrangement of fuel found in a study undertaken after a large
Behaviour of smoke plumes and hazes
layers and the behaviour of the fire and bushfire event in New South Wales (2).
from rural or urban fires
weather conditions. Many of the gaseous
Another study did not find any reduction (Project B 2.1)
aerosols produced in smoke can exist in
in lung function in symptomatic asthmatic
the atmosphere for variable lengths of time This project is enhancing models of smoke
children during the same fires in New South
ranging from days to months and can travel movement and integrating them with other
Wales (3).
considerable distances. meteorological tools, including the Smoke
A recent study conducted in Brisbane Dispersion Forecasting Service, which is
Particulate matter is not as long lived as
has shown that daily respiratory hospital available through the Bureau of Meteorology.
gaseous products and generally only remain
admission rates consistently increased with
in the atmosphere for periods of hours Air Toxics Exposure and measurement
increasing levels of PM10 for both bushfire
to weeks, depending on their size. Most (Project D 2.2)
and non-bushfire periods over a three year
particulate matter emitted by combustion of
period. The findings were also suggestive This project is advancing the knowledge
vegetation consists of elemental and organic
that bushfire smoke was significantly of firefighters’ exposure to such toxic air
carbon and can be categorised according to
associated with increased risk of respiratory pollutants as carbon monoxide, respirable
their aerodynamic diameter: coarse particles
hospital admissions (4). particles, polyaromatic hydrocarbons and
are between 2.5–10 μm (PM10), fine particles
dioxins.
are 0.1–2.5 μm (PM2.5) and ultrafine particles Elsewhere in the world, smoke from the
are less than 0.1 μm. 1997-1998 forest fires in Indonesia resulted It is identifying key toxic pollutants, evaluating
in substantially reduced air quality over their concentration and providing tools to
The coarsest particles in smoke generally
Malaysia, Singapore, Brunei, southern measure, evaluate and control the exposure
settle out from the atmosphere by gravity
Thailand and parts of the Philippines for of firefighters and communities to these
close to the source within hours, the smaller
a number of months (5, 6). This haze was substances. The study is monitoring on the
particles can be dispersed further before
associated with a significant increase in fireground at prescribed burns and wildfires.
settling.
the number of people requiring clinic
Respiratory Health of Firefighters
All particles with an aerodynamic diameter and hospital treatment for smoke-related
(Project D 4)
of less than 10 μm can enter the human symptoms in some studies (7) but not in
respiratory tract, but those particles that are others (8). In the United States, smoke from This project, now complete, investigated the
smaller than 2.5 μm are of particular concern large forest fires have resulted in increased respiratory effects of combustion products as
as they are small enough to penetrate deep hospital visits according to at least three well as the efficacy of the standard issue smoke
into the lungs then enter the blood stream studies (9-11). masks.
and be transported to other tissues.
Three types of masks were tested. One mask
is designed to protect from particulates only,
Sensitive populations
and the other two from both particulates and
Effect of bushfire smoke on Most healthy adults and children will organic volatiles.
human health recover quickly from acute smoke exposure
More information on these projects at:
and not suffer from any long-term adverse
Smoke has been demonstrated to have www.bushfirecrc.com
consequences. However, there are some
significant negative effects on human health
sensitive populations that may experience See also:
from studies investigating the impact of
more severe short- and long-term effects FireNote 3, Smoke and the Control of
tobacco smoke, smoke from indoor wood
from exposure to smoke. Bushfires.
fires and ovens (called indoor biomass
FireNote 12, Firefighter’s Exposure to Air
smoke) and industrial smoke in urban Sensitive populations include:
Toxics During Prescribed Burns.
centres (smog). In these studies, exposure
• individuals with asthma and other
to smoke is usually investigated at a known
respiratory diseases, such as chronic
concentration and for a specified duration.
obstructive pulmonary disease;
In contrast, bushfires and prescribed burning
• individuals with cardiovascular disease
activities episodically expose humans to high
including high blood pressure, coronary
levels of pollutants and for short periods
artery disease, congestive heart failure or
of time. The cause-effect relationship of
angina;
bushfire smoke is therefore more difficult
to investigate. The association between • the elderly as they tend to have pre-
respiratory illness and community exposure existing respiratory and cardiovascular
to smoke from bushfires or prescribed diseases and reduced immune defence
burning has been made in a number of systems against the particulate matter;
Australian epidemiological studies but a
• children inhale more air per kilogram of
causal link is yet to be established.
body weight and as their lungs are still
For example, increased levels of particulates developing, they are more susceptible to
(PM10) in smoke produced by vegetation the effects of air pollution.
2 Fire Note: Bushfire Smoke and Public Health
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