Chapter 4 Climate Impacts and Responses
Impacts of Climate Change on Australia > Disease and human
health
Climate change can affect human health directly through, for
example, heat stress or the consequence of natural disasters, and
indirectly through, for example, disrupted agriculture. Several
of the health impacts of climate change identified by the IPCC
(McCarthy, 2001) are relevant to Australia, including an increase
in vector-, food- and water-borne infectious diseases; a decrease
in winter deaths but an increase in heat-related deaths and
illness; and an increased risk of drowning, diarrhoeal and
respiratory diseases related to any increased flooding.
Australian studies are shedding new light on the likely impact
of climate change on human health. The Federal Government has
funded a formal assessment of the effects of climate change on
health in Australia over the coming decades, entitled Human
Health and Climate Change in Oceania: A Risk Assessment
(McMichael et al., 2002). Each year, 1100 people aged over 65 die
from temperature-related causes (summed in 10 major Australian
cities). The projected rise in temperature for the next 50 years
is predicted to result in a total of three to five thousand
additional heat-related deaths a year (in the absence of adaptive
measures, including the effect of population growth and aging,
and with heat-related deaths defined as deaths estimated from the
overall relationship between temperature and mortality rates from
any cause that are in excess of the average for that time of
year). Temperate cities show higher rates of deaths due to
greater temperature extremes than tropical cities. The estimated
increases in heat-related deaths were predicted to be far greater
than the decreases in cold-related deaths. Canberra may
experience positive effects from a reduced number of cold winter
days in the short-term, but in the medium- to long-term these
health gains are predicted to be outnumbered by additional
heatrelated deaths. The Risk Assessment report also found that 1
in 10 year extreme rainfall events are expected to increase in
almost all Australian states and territories by 2020, changing
the number of floodrelated deaths and injuries to between an
increase of 240% (in the southern areas of New South Wales near
the Murray River) and a decrease of 35% (in north-eastern
Tasmania).
Table 4.2 Australian populations estimated to be living in a
region suitable for dengue transmission (from McMichael et al.,
2003).
| Baseline (million) |
Scenario |
2020 (million) |
2050 (million) |
| 0.17 |
Low: |
| CSIRO Mark 2 |
0.30 |
0.78 |
| ECHAM4 |
0.29 |
0.75 |
| 0.17 |
Mid: |
| CSIRO Mark 2 |
0.33 |
0.77 |
| ECHAM4 |
0.34 |
1.16 |
| 0.17 |
High: |
| CSIRO Mark 2 |
0.51 |
1.24 |
| ECHAM4 |
0.49 |
1.61 |
Malaria is not endemic in Australia, with eradication achieved
in the 1960s (only a handful of cases having been reported since
then). The likelihood of malaria being reintroduced into
Australia is very low – however model results in the health
risk assessment report (McMichael et al., 2003) indicate that
under climate change there is a hypothetical risk of the zone
where Australia’s only malaria vector could exist,
expanding as far south as Rockhampton, Gladstone and Bundaberg if
adaptive measures are not taken. The tourism threat from an
outbreak of vivax malaria in far north Queensland in 2002 and the
recent high incidence of malaria among the Australian defence
forces in East Timor underlines the priority that needs to be
placed on prevention.
From 1991, when national reporting began, to 2002, 2595 cases
of dengue had been recorded. The health risk assessment report
(McMichael et al., 2003) estimated the region climatically
suitable for dengue transmission, accounting for projected
population change but not for the likely adaptive strategies that
would reduce the risk of transmission. The model’s current
risk region, including Broome, Darwin and Katherine in northern
Australia and some coastline between Townsville and Mackay, is
acknowledged as a slight underestimation. The model’s
future risk regions were shown to increase in the simulations, as
given in Table 4.2, although as noted above this does not account
for adaptive measures.
Australian National University researchers have examined
whether climate variables could be used to accurately predict
epidemics of Ross River virus disease. Between 1991 and 2002 in
Australia there were 51,761 notifications of the disease, which
has no treatment (prevention remains the sole public health
strategy). It is well recognised that weather directly affects
the breeding, abundance, and survival of mosquitoes, the
principal vector of many arboviruses. Using weather data from two
regions in southeastern Australia, the scientists assessed Ross
River virus disease data for the period 1991 to 1999. Two
predictable epidemic patterns emerged, after either high summer
rainfalls or high winter rainfalls. Lower than average spring
rainfall in the pre-epidemic year turned out to be a
prerequisite. The research findings are likely to be valuable to
health authorities, as early warning of weather conditions
conducive to Ross River virus disease outbreaks is possible with
a high degree of accuracy in particular regions.
Researchers from Australian National University and Food
Safety Australia have assessed the potential impact of climate
change on food borne disease in the coming century. A link
between climate and microbial food borne disease remains
speculative. However, data show that Salmonella infections
increase in summer, while Campylobacter infections increase in
spring, similar to patterns seen overseas. In eastern Australia,
rates of Salmonella notifications increase with decreasing
latitude and consequently with increasing average yearly
temperature. Food poisoning outbreaks may also be linked to
unusually hot weather which can enhance bacterial replication.
Reports of food poisoning outbreaks are higher during unusually
hot summers in Australia. Assuming that a sustained temperature
rise has a similar effect to monthly temperature variations, then
the incidence of salmonellosis may rise in future decades, and,
by extrapolation, the incidence of diseases caused by other food
borne pathogens and toxins could also rise. Higher global
temperatures could increase human exposure to toxins produced by
cyanobacteria (blue-green algae) in water supplies and
recreational water bodies, which can cause gastrointestinal and
dermatological symptoms. Similarly, production of mycotoxins in
agricultural produce could increase.
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