In
the face of projected climate change scenarios it has become apparent that
societies will need to adapt to sustain the social and ecological systems
on which they rely. Adaptations
are adjustments in practises, processes or structures to take account of changing
climatic conditions. They may be autonomous or policy driven (McCarthy et
al 2001). The tools and techniques for adapting to climate change vary dramatically
and their success will relate to the level in which they address the adaptive
capacity of the community in which they are applied.
The importance of aligning adaptation with adaptive capacity is increasingly
recognized, and we hope that CVAAN will provide opportunities to increase
awareness of the groundbreaking work completed in this area.
Adaptation Planning
Coastal areas have been a particular focus of adaptation planning
for sea level rise and climate change, as well as the relationship of adaptation
to wider coastal management. Climate change is only one of many interacting
stresses in the coastal zone. Thus, when considering adaptation strategies
and planning for increased coastal resilience, other impacts must also be
considered. The ability to deal with multiple stressors is a function of socioeconomic
and environmental condition and existing management arrangements.
The IPCC
technical guidelines for assessing climate change impacts and adaptations
provide a set of technical guidelines (for a range of methods) that enable
comparable estimates of impacts in adaptations in different sectors or regions.
The key tools include general circulation models, scenario data in impacts
assessment, empirical analogue studies, expert judgment, economic models,
biophysical models, and cost-benefit analysis.
Information on types of adaptation planning can be accessed from the UNFCCC
‘Compendium
on methods and tools to evaluate impacts of, vulnerability and adaptation
to, climate change’.
Table 1:
Technologies for adaptation in coastal zones
Protect |
Retreat |
Accomodate |
* Hard
Structures – dykes, sea-walls, tidal barriers, detached breakwaters
* Soft
Structures – dune or wetland restoration or creation, beach nourishment
* Indigenous
options of walls of wood, stone or coconut leaf, afforestation |
*Establishing
set-back zones
* Relocating
threatened buildings
* Phasing
out development in exposed areas
* Creating
upland buffer
* Rolling
easements |
* Early
warning and evacuation systems
* Hazard
insurance
* New
agricultural practices, such as using salt-resistant crops
* New
building codes
* Improved
drainage
* Desalination
systems |
Source: UNFCCC
(2006)
Adaptation
Techniques
There are numerous policy approaches aimed at reducing GHG
emissions and/or enhancing sequestration by sinks, for example; taxes, tradable
permits, subsidies, voluntary agreements, product bans and government investment.
The implementation of policies can be seen as a tool for governments to achieve
certain objectives that they foresee would not be achieved without the implementation
of control mechanisms. Policies can be generic or sector specific. A brief
outline to select policy instruments is presented below.
Economic Instruments
Emission taxes or charges, as the name implies, sees costs attributed to the
levels of emissions produced. Emission taxes do not guarantee a set level
of emissions, so require adjustment to ensure that levels of emissions are
meeting set targets. In a tradable permit system, a number of permits –
equal to the emission limit – are distributed. Each permit-liable entity
is required to hold permits equal to its actual emission level. The tradable
nature of permits makes them a cost-effective means of enforcement, and assuming
compliance, a more reliable means that emission taxes at achieving set emissions
limits.
Policy/ Legal
Regulatory environmental standards set technology standards or performance
standards that are enforced through fines and other penalties. Regulatory
standards may have impacts on economic decision making, however they differ
from market based instruments by specifying technology or performance outcomes
rather than by directly changing prices.
Assessment of the effectiveness of a particular policy instrument follows
the implementation of policies. Alternatively, assessment may be carried out
prior to the implementation of policy instruments to ensure the appropriate
instrument is applied depending on the objective. Commonly, the assessment
of effectiveness is problematic and criteria have been established to evaluate
policy options. The criteria can be broken into three main categories, representing
the ‘triple bottom line’ approach: environment, economy, and society.
Environmental effectiveness refers to the ability of the policy to achieve
the environmental goal, such as a GHG emissions reduction target and its reliability
in achieving that target. Economic effectiveness reviews the ability of the
policy to achieve the environmental goal at the lowest cost, taking transaction,
information, and enforcement costs into account. Social effectiveness examines
how the costs of achieving the environmental goal are distributed across groups
within society, including future generations. Finally, the administrative
and political feasibility of the instrument can be referred to as ‘institutional
effectiveness’. Institutional effectiveness considers flexibility in
the face of new knowledge, general public comprehension, impacts on the competitiveness
of different industries, and other government objectives.
Engineering
As our environment changes, historic development trends are increasingly seen
as inappropriate. Further, as our knowledge of the physical and biological
environment increases; the detrimental impact of human development increasingly
comes to the fore. The response to these discoveries and solutions to accommodate
environmental changes completes with societal social norms and values. Tradeoffs
are made, commonly with the environment adjusted to accommodate the established
social system. One of the key means to adjust or adapt to changing environmental
conditions is through engineering. Engineering typically consists of adjusting
the physical environment to preserve man-made structures and can be classified
into hard and soft approaches. Hard approaches include the construction of
sea walls, dykes and breakwaters. Soft approaches include dune restoration
and beach nourishment. The approach undertaken will depend on the socio-ecological
environment in which it is applied.