12.9. Synthesis
12.9.1 Introduction
Many activities and ecosystems in Australia and New Zealand are sensitive to
climate change, with positive and negative effects. Much climate sensitivity
information is still qualitative, and there are substantial uncertainties in
predictions of regional- to local-scale climate changesespecially rainfall
changes and changes in extreme events. Thus, comprehensive, quantitatively based
cross-sectoral estimates of net Australasian costs of climate change impacts
are not yet available. Confidence remains very low in the impact estimate for
Australia and New Zealand of -1.2 to -3.8% of GDP for an equivalent
doubling of CO2 concentrations (Basher et al., 1998). This estimate
is based on climate change scenarios that are now outdated; does not include
some potentially important impacts, including changes in weeds, pests and diseases,
storm surges, and urban flooding; and does not account for possible adaptations
to climate change.
Despite the uncertainties, there is a large body of knowledge and more agreement
on changes than often is realized (e.g., between different coupled ocean-atmosphere
climate models on the sign of the change in rainfall over large areas of Australia;
see Section 12.1.5.1). There also is qualitative
agreement on reduced water supplies in large agricultural regions of Australia
(see Sections 12.3.1 and 12.5.6).
Potential net impacts on grazing, crops, and forests critically depend on the
balance between the competing effects of warmings, positive or negative rainfall
changes, direct physiological effects of higher CO2 concentrations,
and spatial and temporal variations in soil fertility. We expect with medium
to high confidence that beneficial physiological effects of higher CO2
concentration will become less dominant with time and effects of warming will
become more damaging, especially given the expected tendency toward greater
aridity over much of Australia. Impacts (and thus climate change benefits or
damages) will not scale linearly with increasing GHG concentrations.
The following subsections draw together material from this chapter that is
pertinent to the "policy-relevant questions" identified by the IPCC
Bureau, as well as regional policy concerns.
12.9.2. Observed Consequences of Past and Current Climate Variability in the
Region
Regional consequences documented in this chapter from floods, droughts, and
temperature changes associated with recent ENSO events include losses in the
pastoral agriculture sector from droughts (Australia, 1-2% of GDP; New
Zealand, NZ$422 million estimated farm-gate costs from 1997 to 1999) and impacts
on streamflow, water supply, stream ecology, horticulture, some commercial fisheries,
and toxic algal blooms. Parts of the GBR have suffered mass coral bleaching
from high SSTs (possibly related to ENSO and recent warming trends) and/or lowered
salinity as a result of floods. Storms in the New Zealand region may have been
more frequent in past warm epochs, leading to a greater influx of terrigenous
material onto the continental shelf. Oceanic productivity east of New Zealand
apparently increased immediately prior to and during warm periods 6,000-7,000
years ago and 120,000-125,000 years ago.
Extreme climatic events resulting from natural climatic variability in the
past century have caused major damage and loss of life in Australia and New
Zealand (see Sections 12.1.5.3 and 12.6.2).
These extremes are expected to change in intensity, location-specific frequency,
and sequence as a result of climate change (see Table
3-10 and Section 12.1.5.3), with major impacts
on infrastructure and society unless strong adaptation measures are adopted.
12.9.3. Factors Influencing Vulnerability
12.9.3.1. Abrupt or Nonlinear Changes in Impacts
Several potential abrupt or nonlinear responses to climate change are listed
in Table 12-1. In some cases, they involve a reversal of the sign of the effect
with greater climate change; in others they result from the onset or acceleration
of a biophysical or socioeconomic process that occurs or greatly accelerates
beyond some threshold of climate change. Such thresholds can be quite location-
and system-specific and need to be identified in collaboration between climatologists
and stakeholders. The frequency with which thresholds are exceeded often is
used in engineering in the form of design criteria to withstand an event with
a certain "return period," or average time between occurrences. It
also can manifest itself as a change from an average profit to an average loss
for a given enterprise such as a farm.
Table 12-1: Nonlinear or rapid climate change responses
identified in this chapter. |
|
System |
Description of Change
|
Certainty and Timing
|
Section
|
|
Great Barrier Reef |
Reef death or damage from coral bleaching
|
Medium to high, next 20-50 years |
12.4.7
|
Deep ocean |
Chemical, dynamical, and biological changes from reduction
in bottomwater formation |
Low to medium, century time scale |
12.4.7
|
Southwest of western Australia
|
Rapid loss of species with narrow annual mean temperature
ranges |
High, next 20-50 years |
12.4.2
|
Australian alpine ecosystems |
Loss of species as a result of warming and reduced snow cover |
Medium to high, next 50 years |
12.4.4
|
Insect-borne disease spread |
Conditions more favorable to mosquitoes and other disease
vectors |
High potential, growing vulnerability |
12.7.1
|
Agriculture |
Shift from net profit to loss as a result of increased frequency
of bad years |
High potential in some places, next 20-50 years |
12.8.4
|
Agriculture |
Shift from positive to negative balance between benefits of
increased CO2 and losses from increasing aridity |
High potential in parts of Australia, 50-100 years |
12.5.2, 12.5.3
|
Built infrastructure |
Change in magnitude and frequency of extremes to exceed design
criteria, leading to rapid increases in potential damages to existing infrastructure |
Medium to high in tropical coastal and riverine situations,
next 30-50 years |
12.6.1
|
|
12.9.3.2. Interactions with Other Environmental and Social Factors
Some of the region's ecosystems are extremely vulnerable to invasion by exotic
animal and plant species because of relative isolation before European settlement.
Land-use changes have left some systems and areas more vulnerable to added stresses
from climate changes, as a result of salinization or erosion, and because of
ecosystem fragmentation, which lessens adaptation options for movement of species
threatened by changing habitats (see Section 12.4.8).
Increasing human populations and development in coastal areas and on floodplains
cause increasing vulnerability to tropical cyclones, storm surges, and riverine
flooding episodes (see Sections 12.4.7 and 12.6.4),
which may become more frequent with climatic change. Development has reduced
the area and water quality of many estuaries, increasing the vulnerability of
their ecosystems to sea-level rise and climate changes. Pressures on coral reefs
including the GBR include increased coastal development, fisheries, tourism,
and runoff of nutrients, chemicals, and sediment from land, as well as climate-related
stresses such as rising sea level, rising temperatures, changes in tropical
storm frequency, and acidification of the ocean from increasing CO2
concentrations (see Section 12.4.7).
Poorer communities, including many indigenous settlements, are more vulnerable
to climate-related natural hazards and stresses on health (see Section
12.7.6) because they often are in exposed areas and have less adequate housing,
health, and other resources for adaptation.
Capacity to adapt is a function not only of the magnitude and critical nature
of the climatic change but also of the demographics, economy, institutional
capacity, and technology of a society. Thus, alternative socioeconomic futures
will lead to different capacities to adapt. This has hardly been explored to
date in Australia and New Zealand in relation to climate change.
12.9.3.3. Regional-Global Interactions
Reliance on exports of agricultural and forest products makes the region sensitive
to changes in commodity prices produced by changes in climate elsewhere (see
Section 12.5.9) and to increases in global forests
as a result of carbon sink policies. Other extra-regional factors include increased
risks of invasion by exotic pests, weeds, and diseases; pressures from immigration
from neighboring low-lying Pacific island territories impacted by sea-level
rise (see Section 12.7.6); and international agreements
that constrain net emissions of GHGs. In an era of increasing globalization,
these issues may assume more importance, although this report hardly touches
on them.
|