TECHNOLOGY TO UNDERSTAND AND MANAGE CLIMATE RISKS Background Paper for the UNFCCC Seminar on the Development and Transfer of Environmentally Sound Technologies for Adaptation to Climate Change, Tobago, 14–16 June 2005
Richard J.T. Klein1,2,*, William W. Dougherty3, Mozaharul Alam4 and Atiq A. Rahman4
1 Potsdam Institute for Climate Impact Research, P.O. Box 601203, 14412 Potsdam, Germany Stockholm Environment Institute–Oxford, 266 Banbury Road, Suite 193, Oxford OX2 7DL, UK 3 Stockholm Environment Institute–Boston, 11 Arlington Street, Boston, MA 02116, USA 4 Bangladesh Centre for Advanced Studies, House No. 10, Road No. 16A, Gulshan 1, Dhaka 1212, Bangladesh 2
*
Corresponding author: tel.: +49 331 2882651; fax: +49 331 2882642; e-mail:
[email protected]
Prepared for the UNFCCC Secretariat and the Expert Group on Technology Transfer
FINAL DRAFT 29 August 2005
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Technology is dominated by two types of people: those who understand what they do not manage, and those who manage what they do not understand. — Archibald Putt, 1976
TECHNOLOGY TO UNDERSTAND AND MANAGE CLIMATE RISKS Background Paper for the UNFCCC Seminar on the Development and Transfer of Environmentally Sound Technologies for Adaptation to Climate Change, Tobago, 14–16 June 2005
SUMMARY Many different technologies exist to adapt to natural weather-related hazards. These technologies can also play an important part in reducing vulnerability to climate change. Technologies are available to develop information and raise awareness, to plan and design adaptation strategies, to implement adaptation strategies, and to monitor and evaluate their performance. This background paper briefly describes these four steps and provides important examples of technologies that can be employed to accomplish them, as well as examples of successful case studies. It presents existing frameworks for facilitating the transfer of technologies for adaptation, discusses relevant dimensions of the process of technology transfer for adaptation, and argues that this process should be integrated with national development priorities. The paper’s conclusions are presented as a starting point for more elaborate discussion at the UNFCCC Seminar on the Development and Transfer of Environmentally Sound Technologies for Adaptation to Climate Change, and as a basis for a technical paper that is to follow this background paper.
DISCLAIMER This background paper has been commissioned by the Secretariat of the United Nations Framework Convention on Climate Change. The paper does not necessarily reflect the views of the Secretariat; the responsibility for the text remains with the authors.
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TABLE OF CONTENTS Page 1.
INTRODUCTION .....................................................................................................................1 1.1. 1.2.
Context and Scope of this Paper .....................................................................................1 Relevant UNFCCC Articles, Decisions and Definitions................................................. 2
2.
BACKGROUND....................................................................................................................... 4
3.
ADAPTATION TO CLIMATE CHANGE................................................................................. 5 3.1. 3.2.
4.
TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE .......................................... 9 4.1. 4.2. 4.3. 4.4. 4.5.
5.
The Role of Technology in Adaptation ........................................................................ 10 Information Development and Awareness Raising..................................................... 10 Planning and Design ..................................................................................................... 11 Implementation.............................................................................................................16 Monitoring and Evaluation...........................................................................................19
TECHNOLOGY DEVELOPMENT AND TRANSFER............................................................19 5.1. 5.2. 5.3.
6.
Types of Adaptation ....................................................................................................... 6 The Process of Adapting to Climate Change.................................................................. 7
Frameworks for Facilitating the Transfer of Technologies for Adaptation ................ 20 Dimensions of the Transfer of Technologies for Adaptation ...................................... 22 Integrating Technology Transfer for Adaptation and Development........................... 23
CONCLUSIONS AND WORKSHOP DISCUSSION POINTS............................................... 24
REFERENCES................................................................................................................................ 26 ANNEX 1: TECHNOLOGY TRANFER DECISIONS RELATED TO THE UNFCCC..................... 32
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1.
INTRODUCTION
1.
This background paper aims to provide the Secretariat of the United Nations Framework Convention on Climate Change (UNFCCC) and the Expert Group on Technology Transfer (EGTT) with a summary overview of (i) the current knowledge and understanding of adaptation to climate change, (ii) a framework for assessing technologies for adaptation to climate change, (iii) the process of technology development and transfer as relevant to adaptation to climate change, and (iv) examples of important technologies for adaptation, together with case studies. It may serve as a starting point for a more comprehensive technical paper on the development and transfer of environmentally sound technologies for adaptation to climate change.
2.
The paper should be seen as part of the process to implement Article 4.5 of the UNFCCC, which states that the developed country Parties and other developed Parties included in Annex II shall take all practicable steps to promote, facilitate and finance, as appropriate, the transfer of, or access to, environmentally sound technologies and know-how to other Parties, particularly developing country Parties, to enable them to implement the provisions of the Convention. This commitment is echoed in similar provisions under the Kyoto Protocol (Article 10c).
1.1. Context and Scope of this Paper 3.
This paper is one in a series of publications on technologies for adaptation that have been prepared within the UNFCCC process. An initial report, providing an inventory and assessment of technologies to mitigate and adapt to climate change, was prepared by the UNFCCC Secretariat in 1996 (FCCC/SBSTA/1996/4). It identified what type of information on technologies and know-how would be most useful to the Parties to the UNFCCC. The emphasis of the initial report was on mitigation, reflecting the predominant political interest and the state of knowledge at the time.
4.
Participants in an expert meeting convened by the UNFCCC Secretariat in Amsterdam in 1997 recommended the Secretariat to develop a work programme to prepare to the following papers (FCCC/SB/1997/3): • An overview paper on adaptation; • Focused papers, initially on technologies related to human health, agriculture, coastal zones, urban areas and freshwater resources; • A long-term “vision paper” to set out technological goals in different sectors.
5.
The overview paper was produced as a technical paper in 1997 (FCCC/TP/1997/3). It was followed by one focused paper two years later: a technical paper on coastal adaptation technologies (FCCC/TP/1999/1). In the meantime, the results of a survey of technology and technology information needs of developing countries had become available (FCCC/SBSTA/1998/INF.5).
6.
In response to a request by the Subsidiary Body for Scientific and Technological Advice (FCCC/SBSTA/1995/3), the Intergovernmental Panel on Climate Change (IPCC) prepared a Special Report on Methodological and Technological Issues in Technology Transfer (SRTT), which was published in 2000 (Metz et al., 2000). The SRTT contained two chapters devoted explicitly to adaptation (Human Health and Coastal Adaptation), and other chapters that discussed both mitigation and adaptation (e.g., Agriculture).
7.
At COP-7 in 2001, an Expert Group on Technology Transfer (EGTT) was established, with the objective of enhancing the implementation of Article 4.5 of the UNFCCC, including, inter alia, by analysing and identifying ways to facilitate and advance technology transfer activities and making recommendations to the Subsidiary Body for Scientific and Technological Advice (SBSTA). The EGTT comprises 20 experts, including three members from each of the developing country regions (Africa, Asia and the Pacific, and Latin America and the Caribbean), one from the small island developing states, seven from Annex I Parties and three from relevant 1
international organisations. The progress of work and the terms of reference of the EGTT will be reviewed at COP-12 in 2006. 8.
In 2003 two technical papers were produced, which addressed issues relevant to technology transfer for both mitigation and adaptation. FCCC/TP/2003/1 discussed issues pertaining to capacity-building in the development and transfer of technologies, whilst FCCC/TP/2003/2 analysed enabling environments for technology transfer. In addition, the compilation and synthesis of Annex II National Communications included information with specific reference to technologies for adaptation. In 2004 the UNFCCC Secretariat made available a Compendium on methods and tools to evaluate impacts of, vulnerability and adaptation to climate change.
9.
The EGTT’s programme of work for 2004, endorsed at SBSTA-19 in 2003, includes crosscutting activities, including a proposed action aimed at encouraging the development of environmentally sound technologies, in particular adaptation technologies. As part of the work programme, a draft scoping paper has been prepared by the chairman of the EGTT, outlining the basic concepts of adaptation-relevant technologies. The scoping paper complements Secretariat working paper no. 10 (2003): “Review of Adaptation Activities under the Convention”.
10.
Most recently at COP-10 in 2004, Parties decided to initiate a programme of work on adaptation to climate change (Decision 1/CP.10). The decision emphasises technology transfer for adaptation on an urgent basis in priority sectors. Moreover, it instructs SBSTA to develop a structured five-year programme of work encompassing a range of technology transfer issues.
11.
As a next step, this background paper was meant to stimulate discussion at the UNFCCC Seminar on the Development and Transfer of Environmentally Sound Technologies for Adaptation to Climate Change, which took place in Tobago from 14 to 16 June 2005. In addition, it is expected that the background paper may serve as a starting point for a more comprehensive technical paper on the development and transfer of environmentally sound technologies for adaptation to climate change.
1.2. Relevant UNFCCC Articles, Decisions and Definitions 12.
This subsection reviews the UNFCCC Articles pertinent to the development and transfer of environmentally sound technologies for adaptation to climate change, and lists a number of key decisions made by the Conference of the Parties. In addition, it presents definitions for several of the terms and concepts that are used throughout this background paper.
13.
Articles 3 and 4 of the UNFCCC make various references to adaptation—what it is and how it should be considered—that can be summarised as follows: • Article 3.3 states that Parties should take precautionary measures to anticipate, prevent or minimise the causes of climate change and mitigate its adverse effects. Where there are threats of serious or irreversible damage, lack of full scientific certainty should not be used as a reason for postponing such measures, taking into account that policies and measures to deal with climate change should be cost-effective so as to ensure global benefits at the lowest possible cost. To achieve this, such policies and measures should take into account different socio-economic contexts, be comprehensive, cover all relevant sources, sinks and reservoirs of greenhouse gases and adaptation, and comprise all economic sectors. • Article 4.1, paragraph (b) states that all Parties shall formulate, implement, publish and regularly update national and, where appropriate, regional programmes containing measures to mitigate climate change by addressing anthropogenic emissions by sources and removals by sinks of all greenhouse gases not controlled by the Montreal Protocol, and measures to facilitate adequate adaptation to climate change. Paragraph (e) states that all Parties shall co-operate in preparing for adaptation to the impacts of climate change; develop and elaborate appropriate and integrated plans for coastal zone
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management, water resources and agriculture, and for the protection and rehabilitation of areas, particularly in Africa, affected by drought and desertification, as well as floods. • Article 4.1(f) states that all Parties shall take climate change considerations into account, to the extent feasible, in their relevant social, economic and environmental policies and actions, and employ appropriate methods, for example impact assessments, formulated and determined nationally, with a view to minimising adverse effects on the economy, on public health and on the quality of the environment, of projects or measures undertaken by them to mitigate or adapt to climate change. • Article 4.5 states that the developed country Parties and other developed Parties included in Annex II shall take all practicable steps to promote, facilitate and finance, as appropriate, the transfer of, or access to, environmentally sound technologies and knowhow to other Parties, particularly developing country Parties, to enable them to implement the provisions of the Convention. In this process, the developed country Parties shall support the development and enhancement of endogenous capacities and technologies of developing country Parties. Other Parties and organisations in a position to do so may also assist in facilitating the transfer of such technologies. • Article 4.8 states that the Parties shall give full consideration to what actions are necessary under the Convention, including actions related to funding, insurance and the transfer of technology, to meet the specific needs and concerns of developing country Parties arising from the adverse effects of climate change and/or the impact of the implementation of response measures. • Finally, Article 4.9 states that the Parties shall take full account of the specific needs and special situations of the least developed countries in their actions with regard to funding and transfer of technology. 14.
Annex 1 summarises several key decisions relating to the development and transfer of technologies in the context of the UNFCCC.
15.
Brief definitions of key concepts that are used throughout this background paper are summarised in the paragraphs below. The definitions of the first three concepts are taken from the IPCC Third Assessment Report (TAR; McCarthy et al., 2001). The latter three definitions are taken from the IPCC SRTT (Metz et al., 2000).
16.
Adaptation: Adjustment in natural or human systems in response to actual or expected climatic stimuli or their effects, which moderates harm or exploits beneficial opportunities. Various types of adaptation can be distinguished, including anticipatory and reactive adaptation, private and public adaptation, and autonomous and planned adaptation.
17.
Adaptive capacity: The ability of a system to adjust to climate change (including climate variability and extremes), to moderate potential damages, to take advantage of opportunities or to cope with the consequences.
18.
Vulnerability: The degree to which a system is susceptible to, or unable to cope with, adverse effects of climate change, including climate variability and extremes. Vulnerability is a function of the character, magnitude and rate of climate change and variation to which a system is exposed, its sensitivity and its adaptive capacity.
19.
Technology: A piece of equipment, technique, practical knowledge or skills for performing a particular activity.
20.
Environmentally sound technologies: Technologies that protect the environment, are less polluting, use all resources in a more sustainable manner, recycle more of their wastes and products, and handle residual wastes in a more acceptable manner than the technologies for which they were substitutes. and are compatible with nationally determined socio-economic, cultural and environmental priorities. The term includes hard and soft technologies.
21.
Technology transfer: The broad set of processes covering the exchange of knowledge, money and goods amongst different stakeholders that lead to the spreading of technology for adapting 3
to or mitigating climate change. The word “transfer” encompasses both diffusion of technologies and co-operation across and within countries.
2.
BACKGROUND
22.
Human-induced climate change is caused by the emission of greenhouse gases, which trap longwave radiation in the upper atmosphere and thus raise atmospheric temperatures, as well as produce other changes in the climate system. Carbon dioxide is the most important of these gases and its atmospheric concentration has increased exponentially since the beginning of the industrial revolution as a result of fossil fuel combustion and land-use change. In 1800, the atmospheric concentration of carbon dioxide was about 280 parts per million (ppm); today it is about 350 ppm and rising. Similar increases have been observed for other greenhouse gases such as methane and nitrous oxide.
23.
Projections of future climate change are based on global scenarios of future emissions of greenhouse gases. These emission scenarios are subject to great uncertainty, as they reflect patterns of economic development, population growth, consumption and other factors that are not easy to predict over a 100-year period. A large number of emission scenarios are used to account for this high degree of uncertainty. The most recent emission scenarios, which formed the basis of the climate projections of the IPCC TAR, were published in the IPCC Special Report on Emission Scenarios (SRES; Nakićenović and Swart, 2000) and are known as the SRES scenarios.
24.
For the illustrative SRES scenarios, carbon cycle models project atmospheric carbon dioxide concentrations of 540 to 970 ppm by 2100, with a range of uncertainty of 490 to 1260 ppm (Houghton et al., 2001). Based on these projections and those of other greenhouse gases and sulphate aerosols, the IPCC TAR projects an increase in globally averaged surface temperature of 1.4 to 5.8°C over the period 1990 to 2100, and a global mean sea-level rise of 9 to 88 cm over the same period. These results are for the full range of 35 SRES scenarios, based on a number of state-of-the-art global climate models. The IPCC TAR further states that it is very likely that nearly all land areas will warm more rapidly than the global average, particularly those at northern high latitudes in the cold season (Houghton et al., 2001).
25.
Box 1 provides a succinct overview of the types of impacts that could be expected in agriculture, water resources, forestry, coastal zones, human health and sensitive ecosystems. Climate change will affect many ecosystems and groups and sectors in society, but different ecosystems, groups and sectors will be affected differently, for three important reasons. First, the direct effects of climate change will be different in different locations. Climate models project greater warming at high latitudes than in the tropics, sea-level rise will not be uniform around the globe and precipitation patterns will shift such that some regions will experience more intense rainfall, other regions more prolonged dry periods and again other regions both.
26.
Second, there are differences between regions and between groups and sectors in society, which determine the relative importance of such direct effects of climate change. More intense rainfall in some regions may harm nobody; in other regions it could lead to devastating floods. Increased heat stress can be a minor inconvenience to young people; to the elderly it can be fatal. Extratropical storms can kill tens of thousands of people in South Asia; in the United States they can lead to thousands of millions of dollars worth of damage.
27.
Third, there are differences in the extent to which regions, groups and sectors are able to prepare for, respond to or otherwise address the effects of climate change. When faced with the prospect of more frequent droughts, some farmers will be able to invest in irrigation technology; others may not be able to afford such technology, lack the skills to operate it or have insufficient knowledge to make an informed decision. The countries around the North Sea have in place advanced technological and institutional systems that enable them to respond proactively to sea-level rise; small island states in the South Pacific may lack the resources to avoid impacts on their land, their people and their livelihoods. 4
Box 1: Potential Impacts of Climate Change Agriculture: Growth duration and biological yields of certain crop types would decrease both under rain-fed and irrigated conditions. Subsistence farmers are significantly at risk. Water: Owing to the expected increase in temperature, which in turn would lead to increased evapotranspiration, significantly less runoff relative to observed data is being predicted in many countries. Forestry: Profound shifts in bioclimatic zones are expected in some countries. Some areas in semi-arid countries are expected to be overcome by tropical desert scrub (bush lands / scrublands). Coastal zones: Much infrastructure and economic activity is located in coastal zones, which would be vulnerable to sea-level rise and more frequent extreme weather events (e.g., cyclones, storm surges). Temperature increases could also adversely affect local flora and fauna of coastal areas, as well as the biological equilibrium of marine life. Human Health: Anopheles vectors would increase and with it the incidence and prevalence of malaria in many countries. The appearance of malaria at altitudes close to 2,000 meters is a new phenomenon, but with increasing temperatures, the malaria altitude belt is expected to widen. This could be compounded by the already high incidence and prevalence of diarrhoea, upper respiratory infection and malnutrition. Sensitive Ecosystems: Global climate models predict extreme warming in many ecosystems if greenhouse gas emissions continue to rise. Climate change could endanger the provision of goods and services provided by such ecosystems as forests and woodlands, rangelands, mountainous areas, inland wetlands and arctic regions.
28.
The IPCC TAR noted that the magnitude of the impacts of climate change will depend on a variety of factors, including the magnitude of climate change and the interaction of climate change with other stresses. These other stresses include demographic pressures (e.g., population growth, rural-urban migration patterns) and socio-economic pressures (e.g., globalisation, changing prices of natural resources and energy). In addition, the IPCC TAR noted that the impacts of climate change are likely to be experienced disproportionately by the poorest groups. These groups may include specific populations (e.g., ethnic tribes or nomadic groups) or people with specific livelihoods (e.g., fisherfolk, smallholders or livestock herders).
29.
In Article 4.1(b), the UNFCCC refers to two options to address climate change: mitigation of climate change by reducing greenhouse gas emissions and enhancing sinks, and adaptation to the impacts of climate change. Most industrialised countries have committed themselves, as signatories to the UNFCCC and the Kyoto Protocol, to stabilising greenhouse gas emissions at 1990 levels by the year 2000 and to reducing their overall greenhouse gas emissions by at least 5% compared to 1990 by the period 2008–2012. However, the lag times in the global climate system mean that no mitigation effort, however rigorous, is going to prevent climate change from happening in the next few decades (Wigley, 1998; Pittock and Jones, 2000; Dessai and Hulme, 2001). The warming now being experienced is the result of emissions that took place decades ago. Indeed, the first impacts of climate change are already being observed in natural systems (e.g., Parmesan and Yohe, 2003; Root et al., 2003).
30.
Adaptation is therefore a necessity (Parry et al., 1998). On the other hand, relying on adaptation alone without taking steps to mitigate climate change could well lead to a magnitude of climate change to which effective adaptation is no longer possible, or only at very high social and economic costs. In other words, adaptation to climate change is not an alternative to mitigation. Both are required to reduce the risks of climate change (Burton and Van Aalst, 2004).
3. 31.
ADAPTATION TO CLIMATE CHANGE
In spite of the fact that the UNFCCC refers to both mitigation and adaptation, until recently national and international climate policy focused mainly on mitigation. On the one hand this reflected the concern of some that a stronger focus on adaptation would weaken society’s willingness to mitigate climate change, on the other hand it signified the belief of others that the “invisible hand” of natural selection and market forces would bring about adaptation without the need for policy intervention (Kates, 1997). Since the IPCC TAR established that humans
5
are—at least in part—responsible for climate change and that some impacts can no longer be avoided, academic and policy attention for adaptation has increased sharply (Burton et al., 2002).
3.1. Types of Adaptation 32.
There are various ways to classify or distinguish between adaptation options. First, depending on the timing, goal and motive of its implementation, adaptation can be either reactive or anticipatory. Reactive adaptation occurs after the initial impacts of climate change have become manifest, whilst anticipatory (or proactive) adaptation takes place before impacts are apparent. A second distinction can be based on the system in which the adaptation takes place: the natural system (in which adaptation is by definition reactive) or the human system (in which both reactive and anticipatory adaptation are observed). Within the human system a third distinction can be based on whether the adaptation decision is motivated by private or public interests. Private decision-makers include both individual households and commercial companies, whilst public interests are served by governments at all levels. Figure 1 shows examples of adaptation activities for each of the five types of adaptation that have thus been defined. Anticipatory
Reactive · Changes in length of growing season; · Changes in ecosystem composition; · Wetland migration.
Private
· Purchase of insurance; · Construction of house on stilts; · Redesign of oil-rigs.
· Changes in farm practices; · Changes in insurance premiums; · Purchase of air-conditioning.
Public
Natural Systems
· Early-warning systems; · New building codes, design standards; · Incentives for relocation.
· Compensatory payments, subsidies; · Enforcement of building codes; · Beach nourishment.
Human Systems
Figure 1: Matrix showing the five prevalent types of adaptation to climate change, including examples (Klein, 1998; Smit et al., 2001).
33.
An additional distinction that is often made is the one between planned and autonomous adaptation (Carter et al., 1994). Planned adaptation describes the result of decisions that are based on an awareness that conditions have changed or are about to change, and that some type of action is required to achieve, maintain or return to a desired state. This could, for example, mean building sea walls in anticipation of a rise in sea level, or investing in irrigation in anticipation of dryer conditions.
34.
In contrast, autonomous adaptation refers to the changes that natural and (most) human systems undergo in response to changing conditions in their immediate environment, irrespective of any broader plan or policy-based decisions. Such changes, for example, can be triggered by observed changes in weather patterns that result in shifting market signals or welfare changes (such as the price of crops and the occurrence of diseases). Examples of autonomous adaptations might include changes in farming practices, the purchase of airconditioning devices, insurance policies taken out by individuals and private companies, and changes in recreational and tourist behaviour. Autonomous adaptation in human systems would therefore be in the actor’s rational self-interest, whilst the focus of planned adaptation is on collective needs (Leary, 1999).
35.
Many of the actions taken by individuals, communities and companies as they adapt to climate change are likely to be autonomous (i.e., not requiring external intervention), particularly as such autonomous action has, in the past, been taken in response to variations in climate that have been natural, rather than human-induced. There is currently much interest in whether 6
society can rely on autonomous adaptation to reduce the potential impacts of climate change to an acceptable level, particularly since such initiatives would not require government intervention. In many parts of the world, however, the future impacts of climate change are likely to be significantly greater than those that have been experienced in the past as a result of natural climate variability alone. Such impacts may be more than many of those affected are able to handle effectively with autonomous adaptation, particularly given additional constraints such as limited information, inadequate knowledge, and insufficient access to resources. 36.
As a result, it is now widely acknowledged that there is a need to start planning for adaptation, thus preparing for the impacts of climate change and facilitating and complementing autonomous adaptation initiatives. Article 3.3 of the UNFCCC suggests that anticipatory planned adaptation, as well as mitigation, deserves particular attention. Anticipatory planned adaptation could take the following forms (Klein and Tol, 1997; Huq and Klein, 2003): • Increasing the ability of physical infrastructure to withstand the impacts of climate change. One approach, for example, would be to extend the temperature or rainfall range that a system can withstand; another would be to modify a system’s tolerance to loss or failure. • Increasing the flexibility of potentially vulnerable systems that are managed by humans. This could include allowing for mid-term adjustments in management practices, including changes in use or location. • Enhancing the adaptability of vulnerable natural systems. This could involve reducing stresses due to non-climatic effects, or removing barriers to the migration of plants or animals. • Reversing trends that increase vulnerability. This could range from reducing human activity in vulnerable areas to preserving natural systems that protect against hazards. • Improving public awareness and preparedness. This could include informing the public about the risks and possible consequences of climate change, as well as setting up earlywarning systems for extreme weather events.
3.2. The Process of Adapting to Climate Change 37.
Planned adaptation is best seen as a process entailing more than merely the implementation of a policy or the application of a technology (referred to hereafter as “implementation”. The process of planned adaptation has been described as a multi-stage and reiterative process, involving four basic steps (Klein et al., 1999): • Information development and awareness raising; • Planning and design; • Implementation; • Monitoring and evaluation.
38.
This process of adaptation can be conceptualised as depicted in Figure 2. Climate variability and/or climate change—together with other stresses on the environment brought about by existing management practices—produce actual or potential impacts. These impacts trigger efforts of mitigation to remove the cause of the impacts, or adaptation to modify the impacts. The process of adaptation is conditioned by policy criteria and development objectives, and interacts with existing management practices. It is important to note that Figure 2 represents a simplified decision framework, which does not capture the multitude of actors involved in decision-making, the uncertainty with which these actors are faced, the other interests they have, or the institutional and political environments in which they operate.
39.
It should be noted that adaptation in Figure 2 refers to planned adaptation, aimed at changing existing management practices. Autonomous adaptation is implied in Figure 2 as it determines the manifestation of impacts (Klein et al., 1999). 7
Climate variability
Impacts
Mitigation
Climate change
Information, Awareness
Planning, Design
Implementation
Monitoring, Evaluation
Existing management practices Other stresses
Policy criteria
Development objectives Adaptation
Figure 2: Conceptual framework showing in the shaded area the reiterative steps involved in planned adaptation to climate variability and change.
40.
A key point about Figure 2 is that adaptation to climate change is an ongoing and reiterative process that includes information development, awareness raising, planning, design, implementation and monitoring. Reducing vulnerability requires having mechanisms in place and technologies, expertise and other resources available to complete each part of this process. The mere existence of technologies for adaptation does not mean that every vulnerable community, sector or country has access to these options or is in a position to implement them.
41.
As mentioned in Section 1.2, the IPCC TAR defined adaptive capacity as the “ability of a system to adjust to climate change (including climate variability and extremes) to moderate potential damages, to take advantage of opportunities or to cope with the consequences”. Factors that determine a country’s or community’s adaptive capacity to climate change include its economic wealth, its technology and infrastructure, the information, knowledge and skills that it possesses, the nature of its institutions, its commitment to equity and its social capital (Smit et al., 2001). It is therefore not surprising that most industrialised countries have higher adaptive capacities than developing countries. For example, Bangladesh and The Netherlands share a similar physical susceptibility to sea-level rise, but Bangladesh lacks the economic resources, technology and infrastructure that The Netherlands can call on to respond to the potential impacts (Huq and Klein, 2003).
42.
On the other hand, having adaptive capacity is no guarantee that it is used successfully. In this respect, the development and use of new and existing information are especially important. For example, major coastal development and urbanisation occurred on the east coast of the United States from 1966 to 1989, increasing exposure during a period when hurricane activity was well below average. New inhabitants were often ignorant of the hurricane risk, which became manifest with the more frequent and stronger hurricanes that began with Hurricane Hugo in 1989 (Pielke and Landsea, 1998).
43.
The notion of adaptive capacity has brought to light the importance of considering the linkages between adaptation and development. It is recognised that climate change poses a threat to important development issues such as water supply, food security, human health, natural resources and protection against natural hazards. This recognition has moved adaptation from being the “handmaiden to impacts research in the mitigation context” (Burton et al., 2002) to an activity that is considered crucial within the broader context of sustainable development. The link between adaptation and sustainable development is particularly relevant when seeking to enhance the capacity of countries and communities to adapt to climate change, which is often limited by a lack of resources, poor institutions and inadequate infrastructure, amongst other things (Smith et al., 2003). In addition, the notion of adaptive capacity has helped to demonstrate that adaptation is not a new activity only relevant when addressing climate change, but instead an ongoing process to reduce vulnerability both to today’s and tomorrow’s climate.
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4.
TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
44.
Technologies for adaptation can be considered to include all technologies that can be applied in the process of adaptation, as shown in Figure 2. Alternatively, technologies for adaptation can refer to only those technologies that can be used to implement an adaptation strategy. This section adopts the former definition and provides examples of technologies that can contribute to accomplishing each of the four steps shown in the dark-shaded box in Figure 2, and provides some contextual information on their application.
45.
Technologies for adaptation can comprise “hard” technologies, such as drought-resistant seeds, seawalls and irrigation technology, and “soft” technologies, such as insurance schemes, crop rotation patterns and set-back zones, as well as information and knowledge. A successful adaptation strategy would typically combine hard and soft technologies. For example, an earlywarning system would rely on hard technologies such as measuring devices and information technology, but also on knowledge and skills to strengthen awareness and promote appropriate action when a warning is given. Box 2 summarises a case study on climate information and flood forecasting in Bangladesh. As an example of a hard technology, Box 3 presents a newly developed technology to restore coral growth. Box 2: Early Warning Systems as Adaptation: The Case of Community-based Flood Information Systems in Bangladesh. Every year millions of people in Bangladesh are exposed to catastrophic flooding. When they occur, floods can result in thousands of deaths and can lead to epidemics, as well as seriously habitats, agricultural production, fisheries, and pastoral systems. In rural areas of Bangladesh, disaster preparedness and early warning systems are almost nonexistent. Moreover, millions of people living in coastal communities have little possibility for evacuation from flood prone areas and are highly vulnerable to flood related diseases. The Reducing Risk and Vulnerability to Floods through Community-based Flood Information System (CFIS) Project is an initiative to enhance the adaptive capacity of local Bangladeshi communities regarding the risks of floods and cyclones. The project account for experience throughout the world that has shown that it is local people who are best placed to prepare for and respond to disasters, including floods. The CFIS Project worked in several flood prone coastal districts through partnerships with local organisations and communities. Its goal was the building of an interactive process of monsoon flood information collection and effective dissemination to community stakeholders, thereby increasing the capacity of local communities to adapt to adverse climate phenomena. Prior to the project, most people in the project region would obtain flood-forecast information from a combination of sources: word-of-mouth (i.e., neighbours, relatives, friends), traditional knowledge (i.e., wind, cloud, rain patterns), and local media (i.e., radio, TV, newspapers). The former two information sources are notoriously “hit-or-miss” and have been prone to inefficiencies in communication. Information from local media is ineffective as most people are unable to easily understand media reports and as a result cannot take full advantage of any warnings provided. The CFIS project generated useful flood information during the devastating flood of 2004. The timely and widespread delivery of a flood warning in the project region was widely acknowledged to be helpful in the community response for taking steps to protect crops, habitats, livestock and other support systems. Initial findings of the project were shared in a national workshop just after the flood in September 2004. The Honourable Prime Minister of Bangladesh appreciated the experience of the CFIS project and recommended the concerned agencies including the Disaster Management Bureau to replicate the model in other flood prone areas of the country.
Box 3: Biorock Coral Reef Restoration Technology. A technology for adaptation that shows high potential for reducing the harmful effects of seawater temperature rise and other global warming-related impacts on coral reefs is the “Biorock Process” for mineral accretion. The technology is relatively new and has as its major aim to grow structures and marine ecosystems in seawater, thereby promoting survivability, particularly for coral reefs in regions of high environmental stress. The technology works by applying a low-voltage electrical current through seawater, causing dissolved minerals to precipitate onto surfaces that eventually grow into white limestone structures similar to those materials that make up coral reefs and nourish tropical white sand beaches. Various field tests show evidence that these methods have been successful in the acceleration of coral growth in areas subjected to environmental stresses (e.g., temperatures, pollution, sedimentation) and have produced structures that have been populated by a range of coral reef organisms, such as fish, crabs, clams, octopus, lobster, sea urchins and barnacles. More information on this technology is available at http://www.globalcoral.org/.
46.
In the technical paper that is to follow this background paper, technologies will be presented and discussed in detail for a range of important sectors and systems, including agriculture, water supply, human health, and infrastructure and settlements. The reader is referred to 9
FCCC/TP/1997/3 and to the draft scoping paper by the chairman of the EGTT for summary overviews of technologies for adaptation in various sectors. In addition, compendiums of technologies are being developed by the Provention Consortium and by the secretariat of the International Strategy on Disaster Reduction. Drawing on the chapter “Coastal Adaptation” of the IPCC SRTT (Klein et al., 2000), this section uses technologies for adaptation to sea-level rise and related hazards in coastal zones as an example of the more comprehensive approach proposed for the technical paper. 47.
It should be noted that it is impossible to provide all-inclusive lists of technologies. Rather, the technologies and references listed in this section are meant to be illustrative and to encourage the reader to consider as wide a spectrum of technologies for adaptation as possible.
4.1. The Role of Technology in Adaptation 48.
In many places technology has been instrumental in reducing society’s vulnerability to everpresent weather-related hazards. Extensive research has shown that today’s hazard potential for many sectors and communities will increase because of climate change. However, in many cases the nature of the hazard will not change. Many existing technologies that have proven to be effective in reducing vulnerability to weather-related hazards will therefore also be important as technologies for adaptation to climate change. Technologies may have to be adjusted to meet local needs, and technological development and innovation will continue to increase the effectiveness and efficiency of existing technologies, but given current projections of climate change, successful adaptation is possible without having to rely on the development of new technologies specifically for adaptation.
49.
In addition to the increased hazard potential referred to above, climate change will also pose new challenges to communities and sectors. Adaptation to climate change therefore also involves preparing for situations previously unknown to sectors and communities. Such new situations may arise when trends in temperature, precipitation, sea level and other climate variables exceed critical limits. In these cases technology development and transfer may be particularly important.
50.
Vulnerability to climate change is not only determined by the degree of climate change, but also by the prevailing social, economic and environmental conditions in a community and the existing management practices in a system or sector (see Figure 2). Therefore, successful adaptation to climate change (i.e., actions that reduce vulnerability to the impacts of climate change) may well include actions that are directed at improving such conditions and management practices.
4.2. Information Development and Awareness Raising 51.
Data collection and information development are essential prerequisites for adaptation, particularly to identify adaptation needs and priorities. The more relevant, accurate and up-todate the data and information available to the decision-maker, the more targeted and effective adaptation strategies can be. Coastal adaptation requires data and information on coastal characteristics and dynamics, patterns of human behaviour as well as an understanding of the potential consequences of climate change. In addition, it is essential that there is a general awareness amongst the public of these consequences and of the need to take appropriate action.
52.
Large-scale global and regional data repositories have been established for a great number of climatic and socio-economic variables relevant to coastal zones. These sources of data may be accessed, displayed and downloaded from the Internet. Sea-level data, for example, may be obtained from the Permanent Service for Mean Sea Level (http://www.nbi.ac.uk/psmsl/index. html), the Global Sea Level Observing System (http://www.pol.ac.uk/psmsl/programmes/gloss. info.html) and the University of Hawai’i Sea Level Center (http://uhslc.soest.hawaii.edu/). Additional global data sets can be accessed via the IRI/LDEO Climate Data Library (http:// ingrid.ldeo.columbia.edu/), the ICSU World Data Center (http://www.wdc.rl.ac.uk/wdcmain/), IGBP/IHDP-LOICZ (http://www.loicz.org/), the Center for International Earth Science 10
Information Network (http://www.ciesin.org/) and the IPCC Data Distribution Centre (http:// ipcc-ddc.cru.uea.ac.uk/). The latter centre also provides climate and socio-economic scenarios. 53.
The Global Earth Observation System of Systems (GEOSS), adopted in 2004, complements these data repositories. It represents an international co-operative to enhance preparedness for environmental disasters, bringing together existing and new hardware and software. In addition, the World Meteorological Organisation (WMO) has ongoing weather-watch programmes for short-range weather prediction and emergency response.
54.
Useful as they may be, adaptation to climate change will often require additional, more detailed information than these global data sets and initiatives can provide. Table 1 lists a number of technologies that can serve to increase the understanding of the coastal system (which involves data collection and analysis), to conduct climate impact assessment in coastal zones (so that potential impacts can be quantified for given scenarios) and to raise public awareness (that some form of adaptation is necessary). Many technologies listed in Table 1 represent “soft” options that are vital to building capacity to cope with climatic hazards. Where appropriate, reference is made to publications that either describe the technology in detail or provide examples of its application. Further information on a broad range of technologies for coastal system description can be found in Morang et al. (1997a), Larson et al. (1997), Morang et al. (1997b) and Gorman et al. (1998). Capobianco (1999) discussed technologies in relation to integrated coastal zone management.
55.
Some technologies listed in Table 1 make use of geographical information systems (GIS). GIS combines computer mapping and visualisation techniques with spatial databases and statistical, modelling and analytical tools. It offers powerful methods to collect, manage, retrieve, integrate, manipulate, combine, visualise and analyse spatial data and to derive information from these data. GIS is an example of a technology that is crosscutting, in the sense that it contributes not only to information development and awareness raising but also to the other three steps shown in Figure 2. Collected data can be stored in a GIS, combined to develop new insights and information, and visualised for interpretation and educational purposes.
4.3. Planning and Design 56.
When the available data and information point towards a potential problem that would justify taking action, the next stage is to decide which action could best be taken and where and when this could best be done. The answers to these questions depend on the prevailing criteria that guide local, national or regional policy preparation, as well as on existing development and management plans that form the broader context for any adaptation initiative. Important policy criteria that could influence adaptation decisions include cost-effectiveness, environmental sustainability, cultural compatibility and social acceptability. In addition, countries may choose to take a precautionary approach when postponing action would involve substantial risks, even though uncertainty may still be considerable.
57.
Planners will always face a certain degree of uncertainty, not only because the future is by definition uncertain, but also because knowledge of natural and socio-economic processes is and always will remain incomplete. This uncertainty requires planners to assess the environmental and societal risks of climate change with and without adaptation (Carter et al., 1994). The information thus obtained can help to determine the optimal adaptation strategy and timing of implementation. There are a number of decision tools available to assist in this process. Examples of these tools include cost-benefit analysis, cost-effectiveness analysis, riskeffectiveness analysis and multi-criteria analysis. The latter technique is particularly relevant when great significance is attached to values that cannot be easily expressed in monetary terms.
11
Awareness Raising • Printed information • Audio-visual media • Interactive tools
• Integrated assessment
• (Semi-) quantitative methods
Climate Impact Assessment • Index-based methods
• Absolute sea level
-
-
Brochures, leaflets, newsletters Newspapers, radio, television, cinema Board-games Internet Computerised simulation models
Coastal vulnerability index Sustainable capacity index IPCC common methodology Aerial-videotape assisted vulnerability assessment UNEP impact and adaptation assessment Coupled models
- Historical and geological methods - Satellite remote sensing - Tide gauges, satellite altimetry, global positioning systems - Historical and geological methods • Past shoreline positions - Airborne and satellite remote sensing • Land use - Resource surveys • Natural values - Mapping and surveying • Socio-economic aspects • Legal & institutional arrangements - Interviews, questionnaires • Socio-cultural factors - Interviews, questionnaires
Mapping and surveying Videography Airborne laserscanning (lidar) Satellite remote sensing Waverider buoys Satellite remote sensing Tide gauges Tide gauges
Technology
Coastal System Description • Coastal topography & bathymetry • Wind and wave regime • Tidal and surge regime • Relative sea level
Application
12
-
-
-
-
Hughes and Brundrit (1992); Gornitz et al. (1994); Shaw et al. (1998) Kay and Hay (1993); Yamada et al. (1995); Nunn et al. (1994a,b) IPCC CZMS (1992); Bijlsma et al. (1996) Leatherman et al. (1995); Nicholls and Leatherman (1995) Klein and Nicholls (1998, 1999) Engelen et al. (1993); Ruth and Pieper (1994); West and Dowlatabadi (1999)
Birkemeier et al. (1985, 1999); Stauble and Grosskopf (1993) Debusschere et al. (1991); Holman et al. (1994); Plant and Holman (1997) Lillycrop and Estep (1995); Sallenger et al. (1999) Leu et al. (1999) Morang et al. (1997a) Martinez-Diaz-de-Leon et al. (1999) Pugh (1987); Zhang et al. (1997) Emery and Aubrey (1991); Woodworth (1991); Gröger and Plag (1993); Nicholls and Leatherman (1996); NOAA (1998) Van de Plassche (1986) Nerem (1995); Fu et al. (1996); Nerem et al. (1997); Cazenave et al. (1998) Douglas (1991); Baker (1993); Miller et al. (1993); Zerbini et al. (1996); Neilan et al. (1997) Crowell et al. (1991); Beets et al. (1992); Crowell et al. (1993); Moore (2000) Redfern and Williams (1996); Clark et al. (1997); Henderson et al. (1999) Lipton and Wellman (1995); Turner and Adger (1996) Penning-Rowsell et al. (1992) English Nature (1992) Tunstall and Penning-Rowsell (1998); Tunstall (2000)
Additional Information
Table 1: Examples of important technologies to collect data, provide information and increase awareness for coastal adaptation to climate change. Note that this table is not intended to provide an exhaustive list of applications and technologies (Klein et al., 2000, 2001).
58.
In combination with scenarios of relevant developments and models to assess and evaluate changes in important natural and socio-economic variables (including climate), GIS can assist planners in identifying appropriate technologies for adaptation, as well as the optimal locations for their application, depending on the criteria of the decision-maker. One simple, first-order application of GIS in coastal adaptation would be overlaying scenarios of sea-level rise with elevation and coastal development data to define impact zones. More sophisticated applications may include the modelling of morphodynamic and ecological responses to climate change. In addition, GIS allows for the non-invasive, reversible and refinable testing of specific technologies for adaptation before these are implemented in the real world. After implementation, newly acquired data can be analysed to evaluate technology performance. Once created, a GIS database will have further utility in other aspects of management and policy.
59.
The modelling of potential futures based on plausible scenarios is particularly pertinent for the planning and design of technologies for adaptation, when relevant impacts are quantified, alternative adaptation options are evaluated and one course of action is selected. Climate impact assessment requires models of relevant changes in morphological, ecological and human factors, as well as their interaction over appropriate time scales (i.e., a decade or longer). The necessary modelling capabilities are increasing rapidly and current developments in information technology are facilitating the transfer and application of these tools as they are developed. However, the limitations inherent in all models (i.e., they are representations of a part of reality for a specific purpose) must not be overlooked. Human expertise and interpretation remain essential for the intelligent use of any model.
60.
The quality and effectiveness of the planning and design process is influenced by the context in which decisions are made. For example, coastal management in many countries used to be topdown by nature, but as public interest and involvement in coastal issues have grown, so has resistance to top-down decision-making (e.g., Taiepa et al., 1997). The successful implementation of many coastal policies, including adaptation to climate change, is now increasingly dependent on public acceptance at the community level. Hence, in addition to informing the public so as to raise their awareness of the issues at stake (see Section 4.2), it is also important to involve them throughout the planning process. Gaining public acceptance is an important prerequisite for identifying and transferring appropriate technologies for adaptation. Further, local expertise will be required for successful technology implementation, application, maintenance and enforcement.
61.
Box 4 shows how the combination of local stakeholder involvement, perceived vulnerability and prudent planning and design can lead to adaptation solutions that meet strategic near- and long-term climate-related challenges.
62.
In some settings, however, public involvement can be difficult to accomplish. In situations where there is little truly private land, coastal inhabitants may have little long-term stake and therefore interest in the land they occupy (e.g., in parts of Tonga; Nunn and Waddell, 1992). Further, governments may have neither the resources to address countrywide coastal or other forms of natural resource management nor, compared to long-resident inhabitants, the local knowledge or experience that are essential for effective management (e.g., in parts of Fiji; Nunn et al., 1994a).
63.
In response to the difficulties encountered in planning and designing adaptation strategies, a number of frameworks have been developed to assist in these activities. One recent decision framework that has relevance to the planning and design of adaptation is UNDP’s Adaptation Policy Framework (APF; Lim and Spanger-Siegfried, 2005). The APF is intended to complement existing policymaking related to climate change in developing countries, including processes of assessment, project development and monitoring. It is structured around the following four major principles: • Adaptation to short-term climate variability and extreme events is explicitly included as a step towards reducing vulnerability to longer-term climate change; • Adaptation policy and measures should be assessed within a developmental context;
13
• Adaptation occurs at different levels in society, including the local level; • Both the strategy and process by which adaptation activities are implemented are equally important. Box 4: Factoring future climate change in today’s decisions: The case of Boston Harbor Some planning agencies are beginning to incorporate future climate change in current decision-making. An interesting example comes from Massachusetts in the USA, where the Massachusetts Water Resource Authority (MWRA) has installed a sewage treatment plant for the greater Boston metropolitan area with climate change—and in particular accelerated sea-level rise—in mind. Even before the arrival of English and European settlers, the Boston Harbor was an important natural resource with local Native Americans fishing and planting crops along the coasts of the 30 or so islands that dot the Harbor. In the early 1600s the Massachusetts Bay Company landed and began settling the area, clearing land for livestock and firewood. Boston Harbor quickly became a busy trading port and by 1660 almost all English imports to New England came through these waters. As Boston grew and flourished over the next 300 years, however, the city's waste began to exert a toll on the Harbor. Those treatment plants that were installed only performed primary sewage treatment, not secondary treatment, and the facilities were often overloaded. By the early 1980s the media was calling Boston Harbor the filthiest harbor in the nation. As a result of litigation initiated by a private citizen, the courts ordered the city of Boston to build a new secondary treatment plant, and carry out a subsequent cleanup of the Harbor. Deer Island, located within the Harbor, was selected as the site for the sewage treatment plant. The design called for raw sewage collected from communities on shore to be pumped under Boston Harbor and then up to the Deer Island treatment plant. After waste treatment, the effluent would be discharged into the Harbor through a downhill pipe. In order to reduce the costs of pumping untreated sewage from the shore up to the Deer Island treatment plant, the MWRA originally planned to lower the level of the Deer Island plant about half a metre to be closer to sea level. However, design engineers were concerned that sea-level rise would necessitate construction of a wall around the treatment plant to keep the sea out. The effluent would then need to be pumped up over the wall and into the Harbor. Such a pump would cost several hundred million dollars. To avoid such a cost, even though it might be decades before it would need to be installed, the designers decided to leave the island at a higher elevation. In 1998 the Deer Island treatment plant was completed. Three points deserve special mention concerning the proactive adaptation planning by the MWRA. First, the decision by the MWRA to account for climate change will also enhance the resilience of the Harbor treatment system under current climate variability from storm surges (Weiner (1993) found the 10-year surge elevation in Boston Harbor to be 2.8 metres, the 100-year surge elevation to be 3.16 metres and the 500-year surge elevation to be 3.41 metres). Second, while the planning involved was proactive and innovative, the pump technology involved was conventional and readily accessible. Finally, the Boston Harbor has become progressively cleaner with native fish species like smelt, herring, striped bass and bluefish returning to the Harbor, as well as porpoises and seals.
The APF is comprised of five basic steps, each of which is linked to two important crosscutting issues, as shown in Figure 3.
1. Project scope and design 2. Assessing current vulnerability 3. Characterizing future climate risks 4. Developing an adaptation strategy 5. Continuing the adaptation process
Figure 3: Outline of the APF process.
14
MEASURING AND ENHANCING A DAPTIVE
APF Steps
STAKEHOLDER ENGAGEMENT
64.
65.
Since specific adaptation measures are usually implemented at the local level, the APF is also intended to be accessible to the private sector, the general public and other stakeholders. The APF is capable of yielding a variety of outputs, depending on how it is applied. Whilst specific outputs depend on particular needs and goals, in general, a completed APF process leads to a clarification of adaptation strategies, policies and/or technology measures that a country could implement. These strategies, policies and measures can be aimed at different levels of society, as well as at different spatial and temporal scales. Their general purpose will be to reduce the potential negative impacts and exploit the opportunities of climate variability and change, and to enhance adaptive capacity.
66.
Another decision framework that has particular relevance to adaptation to climate change is the Technology Needs Assessment (TNA). A TNA handbook has been developed by UNDP that provides an overview of the process of technology identification/selection as it applies to mitigation and adaptation (Gross et al., 2004). From an adaptation perspective, technology needs assessment is intended to help to prioritise technologies, practices and policy reforms that can be implemented in different sectors of a country to adapt to climate change. Technology needs assessment—with its emphasis on identification and selection of technology—is fundamental to the process of technology transfer and can be seen as part of an overall integrated framework to promote technology transfer.
67.
Carrying out a technology needs assessment takes into consideration six essential activities: • Preparation of an initial list of options; • Development of criteria for assessment; • Prioritisation of key sectors; • Identification of barriers; • Selection of options; • Preparation of a synthesis report.
68.
Within this broad framework, there are some additional steps that are specific to the nature of the adaptation process itself. These include the identification of vulnerable sectors and groups, the development of criteria for prioritisation of vulnerable sectors and groups, characterisation of prioritised sectors and groups, assessment of local capacity to use technologies for adaptation, and selection of options. There are two issues—stakeholder engagement and barriers analysis— that cut across all these activities and are integral to the successful implementation of a technology needs assessment.
69.
The TNA process overlaps the simplified decision framework shown in Figure 2 in two ways. First, the six essential activities of a TNA fit squarely within the information awareness and planning/design phases of Figure 2. This means that any effort to modify the impacts of climate change through technology transfer and application would involve initial activities that are defined in large part by the process of undertaking a TNA. Second, the policy criteria and development objectives inputs to the planning/design activities in Figure 2 can be largely obtained from carrying out the additional TNA steps specific to the adaptation process. This means that specific TNA activities involving the development of criteria for prioritisation of vulnerable sectors and groups, characterisation of prioritised sectors and groups, and assessment of local capacity for the use technologies for adaptation can help to meet broad planning and design objectives.
70.
As an example showing the intersection between TNA and Figure 2, Box 5 provides examples of the types of technologies for adaptation in agriculture, water resources and coastal zones that emerged from a TNA for adaptation conducted in Mauritius (TT:CLEAR). The research, stakeholder discussions and the resulting consensus that emerged around the specific technologies highlight the important role of TNA in promoting awareness raising, as well as merging technology identification and selection with planning and design objectives
15
Agric
Box 3: Mauritius' TNA for adaptation results Extension of irrigation facilities Introduction of hydroponics culture Cultivation in greenhouses and under cover Increasing Surface Storage Capacity
Water Resources
Reduce Loss of Surface Runoff to the sea Desalination (conversion of seawater into potable water) Efficient water pricing Recycling Waste Water Increase Use of Gray Water for secondary household purposes Increase Irrigation Use Efficiency by shifting centre pivot and drip techniques Reduce Leakage by rehabilitating distribution systems Increase Drought Toleration through drought tolerant cultivars Replacement Casements Setback Building Distance Inland flood defences Flood warning systems
Coastal Zones
Better management of rain / waste water Building with 'nature' techniques Stimulate growth of coral reefs naturally or artificially Hand-placed rock sea walls Gabion walls Groynes Revetments Bulkheads and seawalls Breakwaters Storm surge barriers Flooding and storm drains Beach nourishment
71.
A third recent decision framework that has relevance to the planning and design of technologies for adaptation is the National Adaptation Programme of Action (NAPA) process, which emerged from COP-7 in 2001. The NAPA process is being implemented in the least-developed countries. It is intended to yield a concise document that specifies a list of priority activities that communicate the immediate and urgent needs of vulnerable communities, resources, or systems, considering their low adaptive capacity to climate change. The NAPA process seeks to ensure adequate stakeholder representation, identify a set of climate change adaptation initiatives, establish country-driven criteria by which to evaluate and prioritise adaptation initiatives, make consensus-based recommendations for adaptation activities, and as needed, recommend capacity building, and policy, programme and institutional integration, as part of adaptation priority activities.
72.
One key feature of the NAPA process is the role of stakeholder consultations for establishing priority vulnerabilities and potential technologies for adaptation. Together with an assessment of national development plans, the stakeholder consultation process is intended to link experts and local groups for weighting and ranking of potential adaptation projects and technologies. Once prioritised, specific information, such as geographical location, institutional weaknesses and strengths, should be identified, as such characteristics are important to define resilient features, competing interests and uses, overlap with other sectors and opportunities to create synergies (e.g., adaptation measures taken in one sector that have indirect benefits in another sector).
4.4. Implementation 73.
Once all options for coastal adaptation have been considered and the most appropriate strategy has been selected and designed, implementation of the strategy is the next stage. An adaptation 16
strategy can include the application of technology, but this does not have to be the case. In coastal zones, an adaptation strategy to sea-level rise can comprise one or more options that fall under the three broad categories protect, retreat and accommodate (IPCC CZMS, 1992). Table 2 provides an overview of these options and the technologies that make them possible (see also NRC, 1987; IPCC CZMS, 1990; Bijlsma et al., 1996). It should be noted that, in addition to the subdivision between protect, retreat and accommodate, there are various other ways to classify or distinguish between different adaptation strategies, both in generic terms (e.g., Smit et al., 2000) and for coastal zones (e.g., Kay et al., 1996; Pope, 1997). 74.
Klein and Nicholls (1998) concluded that most of the options listed in Table 2 require strategic planning, whereas few would occur autonomously. In addition, options to protect against sealevel rise can be implemented both reactively and proactively, whilst most retreat and accommodation options are best implemented in an anticipatory manner. To date, the assessment of possible adaptation strategies in coastal zones has focused mainly on protection. Bijlsma et al. (1996) noted the need to identify and evaluate the full range of options listed in Table 2. The range of appropriate options will vary amongst and within countries, and different socio-economic sectors may prefer competing adaptation options for the same area. The existence of such a broad range of options is one of the reasons why adaptation to climate change is recommended to take place within the framework of integrated coastal zone management (see also Section 5.3).
75.
Table 2 combines hard technologies, such as dikes, levees and floodwalls, and soft technologies, such as evacuation systems. Note that there are also a range of applications that require only limited technology, such as increasing or establishing set-back zones and creating upland buffers.
76.
In the process of adapting to climate change, one of the critical components is the presence of appropriate and effective institutions. Institutions vary widely across scales (small to large, local to national), sectors (such as agriculture, water, forestry, transport) and from formal (e.g., Ministry or Department of Environment, NAPA Secretariat) to informal (e.g., a local village community). Whilst formal institutions can respond to adaptation needs and challenges within its regulations, institutional guidelines and allocated resources, informal institutions often respond to specific adaptation challenges such as drought, flood or a cyclone as self-organised and self-motivated systems. In between these two extremes there is a range of institutional arrangements and different degrees of formalisation. For example, NGOs can play important roles in advancing technologies for adaptation.
77.
In most countries and ecosystems, indigenous knowledge of communities has been accumulated into experiences of responses to different climate-related challenges. Flood- or drought-affected areas have often evolved local-level technologies for adaptation that can be of great value to areas likely to be affected by similar events. Hence there is a need to assess these indigenous technologies and community-level response strategies. Successful and appropriate technologies may be replicated and adopted in the areas likely to be affected by climate change.
78.
The relevant institutions need to have their mandates ascertained so that they can respond to the needs of advancing technologies for adaptation. Further, skilled manpower, well-developed and tested tools and methodologies need to be established and resourced. For institutions to succeed in assisting adaptation, they themselves must be responsible and flexible. These institutions should be able to interact, involve and be guided by stakeholders such as communities, farmers, fisherfolk, local NGOs, local-level government agencies, amongst others. There is a need for adequate and continuous funding so that key institutions are well established and prepared to advance technologies for adaptation and meet the needs of the different stakeholders.
17
- Titus et al. (1987) - Titus et al. (1987) - Ribeiro (1996)
- Increased diameter of pipes - Increased pump capacity - Desalination plants
• Desalination
18
- Evacuation systems - Limited technology required - Various technologies (e.g., aquaculture, salineresistant crops), depending on location and purpose - Various technologies - FEMA (1986, 1994, 1997) - Limited technology required - May et al. (1996)
- Penning-Rowsell and Fordham (1994); Haque (1995, 1997); Handmer (1997); Rosenthal and ’t Hart (1998); Elliot and Stewart (2000) - Parker and Handmer (1997); Rosenthal and ’t Hart (1998) - Davison (1993); OTA (1993); Crichton and Mounsey (1997); Clark (1998); Arnell (2000)
- Early-warning systems
Accommodate • Emergency planning
• Hazard insurance • Modification of land use and agricultural practices • Modification of building styles and codes • Strict regulation of hazard zones • Improved drainage
- Titus (1991, 1998) - Burd (1995); English Nature (1997); French (1997, 1999) - Kaly and Jones (1998)
- Limited technology required - Various technologies, depending on location - Limited technology required
- McLean et al. (1998); Mimura and Nunn (1998)
- NRC (1990); Kay (1990); Owens and Cope (1992); Caton and Eliot (1993); OTA (1993) - Rogers (1993) - OTA (1993); DETR (2000)
Dune restoration and creation Wetland restoration and creation Afforestation Coconut leaf walls Coconut fibre stone units Wooden walls Stone walls
-
- Gilbert and Horner (1984); Kelly (1991); Penning-Rowsell et al. (1998) - Sorensen et al. (1984) - Delft Hydraulics and Rijkswaterstaat (1987); Davison et al. (1992); Stauble and Kraus (1993); Hamm et al. (1999) - Doody (1985); Vellinga (1986); Nordstrom and Arens (1998); Nordstrom et al. (1998) - NRC (1992, 1994); Boesch et al. (1994); Tri et al. (1998)
- Pilarczyk (1990); Silvester and Hsu (1993)
Additional Information
- Limited technology required - Various technologies - Limited technology required
Dikes, levees, floodwalls Seawalls, revetments, bulkheads Groynes Detached breakwaters Floodgates, tidal barriers Saltwater intrusion barriers Periodic beach nourishment
-
Technology
(Managed) Retreat • Increasing or establishing set-back zones • Relocating threatened buildings • Phased-out or no development in exposed areas • Presumed mobility, rolling easements • Managed realignment • Creating upland buffers
• Indigenous options
• Soft structural options
Protect • Hard structural options
Application
Table 2: Examples of important technologies to protect to, retreat from or accommodate sea-level rise. This table is not intended to provide an exhaustive list of applications and technologies (Klein et al., 2000, 2001).
79.
In countries with climate-related insurance markets, insurance can have a positive or a negative role in promoting adaptation to climate change and any associated technology transfer. This may happen directly via contacts with customers or indirectly as the insurance industry lobbies institutions. Technology underpins this interaction as improving data management and modelling capability give the insurance industry more detailed information of both the risks and opportunities that climate variability and change present. However, more knowledge may benefit the insurance industry, but it does not necessarily lead to overall social benefits. Clark (1998) argued that partnerships between governments and the insurance industry can benefit both the industry and wider society in terms of reduced exposure and maintain the long-term viability of the insurance industry.
4.5. Monitoring and Evaluation 80.
It is recommended practice in any field of policy that the performance of implemented measures is periodically or continuously evaluated against the original objectives. Such evaluation can yield new insights and information, which could give rise to adjust the strategy as appropriate. This process is illustrated in Figure 2 by the feedback loop from evaluation within the shaded box. This evaluation must be distinguished from the evaluation exercise that is done to identify the most appropriate technology, and which is part of the planning and design phase (Section 4.3).
81.
Effective evaluation requires a reliable set of data or indicators, to be collected at some regular interval by means of an appropriate monitoring system. Indicators are a tool for reporting and communicating with decision-makers and the general public. They should fulfil a range of properties, including (i) a relationship to functional concepts, (ii) be representative and responsive to relevant changes in conditions, and (iii) be easily integrated within a broader evaluation framework. Evaluation is an ongoing process and the monitoring should be planned accordingly. There is limited experience of such long-term monitoring, so in many situations it is unclear which are the most appropriate data or indicators (Basher, 1999).
82.
For coastal physical systems, experience can be drawn from countries where the coast has been monitored for long periods. In The Netherlands, for instance, the position of high water has been collected annually for nearly a century and cross-shore profiles have been measured annually since 1963 (Verhagen, 1989; Wijnberg and Terwindt, 1995). Observations of the “natural” evolution of the coast allow trends to be reliably estimated and hence the impact of human interventions on the coast (breakwaters, nourishment, etc.) to be evaluated.
83.
In general, the technologies to be used for monitoring are the same as those used for initial description of the coastal system. They are therefore listed in the upper part of Table 1 and discussed by Morang et al. (1997a), Larson et al. (1997), Morang et al. (1997b) and Gorman et al. (1998).
5. 84.
TECHNOLOGY DEVELOPMENT AND TRANSFER
To enhance the development and transfer of environmentally sound technologies to address climate change requires an understanding of whether mitigation or adaptation objectives are being sought. The particular processes to assess technology needs in these two areas—whilst fundamentally consistent and overlapping in some key areas—are operationally distinct in others. The assessment and transfer of environmentally sound technologies for mitigating climate change is fairly straightforward, in the sense that such technologies have a clear objective: to reduce or avoid greenhouse gas emissions. They tend to target specific, well-known emitting sectors such as power generation, transportation and industrial operations. Moreover, there is a large literature of mitigation technology applications from which lessons can be learnt and taken into account when assessing such technologies in various local contexts.
19
85.
The assessment and transfer of environmentally sound technologies for adaptation to climate change pose a more complex challenge, at two distinct levels. First, there is inherently more uncertainty regarding vulnerability and subsequently, adaptation to the impacts of climate change. This uncertainty is manifested most acutely at the local level and carries over to the identification of appropriate adaptation measures, options and technologies, as well as to the stakeholders that are affected. Therefore, hard technologies may not be appropriate and hence the relevance and importance of soft technologies as discussed earlier. Second, adaptation concerns have only recently become a focus of climate change negotiations. Unlike mitigation, which can claim a formal protocol as a framework for North-South co-operation on reducing greenhouse gases (i.e., the Kyoto Protocol), there is no comparable approach for focused international co-operation in the adaptation area. As a result, there are limited examples of realworld successes from which to draw lessons.
86.
Technology transfer is a complex process that involves multiple stakeholders, a variety of perspectives, and is highly interdisciplinary. It encompasses diffusion of technologies and cooperation across and within countries. It covers technology transfer processes between developed countries and developing countries, amongst developed countries, amongst developing countries and amongst countries with economies in transition. Finally, technology transfer comprises the process of learning to understand, utilise and replicate the technology, including the capacity to choose it and adapt it to local conditions and integrate it with indigenous technologies.
87.
Although there have been numerous frameworks and models put forth to cover different aspects of technology transfer, there are no corresponding overarching theories (IPCC, 2000). In this section, the emphasis is on exploiting opportunities for transferring technologies for adaptation as represented in various multilateral and bilateral frameworks, understanding the various dimensions for promoting the transfer of technologies for adaptation, and making the overall process more integrated in national development processes.
5.1. Frameworks for Facilitating the Transfer of Technologies for Adaptation 88.
Frameworks for the transfer of technologies for adaptation exist in the form of multilateral environmental agreements (MEAs), which are linked with multilateral agencies that have clear development goals such as the United Nations Development Programme, the World Bank, and regional development banks. These organisations support technology transfer as a way of achieving country-driven goals in implementing the various MEAs. In addition, there are numerous bilateral assistance frameworks that donor countries have established to encourage technology transfer via development assistance. These frameworks can support a range of development and political goals, often including the expansion of foreign markets for exports and the expertise of national firms.
89.
In addition to the UNFCCC, there are several other multilateral environment and development frameworks that are either relevant to or conducive to the transfer of technologies for adaptation. These frameworks are represented—legally as well as operationally—by two major international environmental agreements (MEAs): the Convention on Biological Diversity (CBD) and the United Nations Convention to Combat Desertification (UNCCD). Several other MEAs have potential as frameworks within which technologies for adaptation are implied. The implementation of each of these MEAs has evolved along quite distinct paths over the years in signatory countries, with different communication products, institutional leads, and schedules for implementation.
90.
In the course of preparing this background paper, a sampling of several country-specific action plans (i.e., Eritrea, Ethiopia, Yemen and Sudan) emerging from MEA implementation have been considered in order better to assess a range of activities where potential synergies may exist. The reviewed action plans contain a variety of measures, initiatives and technologies that contribute directly to the goals of the particular MEA. It is important to note that many of these same measures, initiatives and technologies also contribute implicitly to meeting adaptation goals 20
through their enhancement of local capacity to cope with climate hazards. In other words, there are opportunities for actions taken under the various MEAs to complement actions taken to promote the transfer of hard and soft technologies for adaptation to climate change. 91.
Table 3 illustrates this point, summarising the various sectors that would benefit from the implementation of National Action Plans for the MEAs. These sectors have strong overlap with the sectors that are likely to experience significant impacts of climate change (see Box 1). The overlap suggests that the overall process of technology transfer will likely include specific initiatives that could be credited as meeting climate change adaptation goals. Considering the transfer of technologies for adaptation within the broader MEA framework will enhance the opportunities for exploiting the range of positive synergies across the initiatives and help to build local adaptive capacity. Multilateral Environmental Agreement
Sectors affected
Convention on Biological Diversity
Forestry, coastal zones
Convention to Combat Desertification
Agriculture, forestry
Cartagena Protocol on Biosafety
Agriculture, human health
Convention on International Trade in Endangered Species (CITES) Agriculture, coastal zones, forestry, water resources Convention on the International Maritime Organisation
Coastal zones
World Heritage Convention
Coastal zones, forestry
Table 3: MEAs potentially relevant to the transfer of climate change–related technologies for adaptation.
92.
Another important framework for technology transfer for adaptation exists in the form of bilateral development assistance. Particularly for the poorest developing countries, which happen to be the most vulnerable to climate change, development assistance remains a main conduit for government supported technology transfer efforts (IPCC, 2000). Such assistance needs to be developmental and concessional meaning that aid flows in the form of grants and/or low-interest loans. Whilst there are 21 OECD member governments (out of 26) that have development assistance programmes, there are three—Canada, Germany and the Netherlands— that have programmes specifically targeted to climate change adaptation, as described below.
93.
In 2000 Canada established a fund dedicated to helping developing countries achieve their commitments as stated in Article 4 of the UNFCCC. Through the Canada Climate Change Development Fund (CCCDF), Canada helps people in developing countries to address climate change in four ways: (i) introducing policies and technologies that will reduce harmful greenhouse emissions; (ii) promoting forestry and agriculture practices that will protect and enhance carbon sinks; (iii) reducing the vulnerability of people in developing countries to climate change and helping them adapt to its negative effects; (iv) raising awareness and helping to develop tools and technologies to combat climate change. The CCCDF is a five-year, $100 million initiative administered by CIDA.
94.
Germany’s Climate Protection Programme for Developing Countries (CaPP) focuses on both mitigation and adaptation to climate change. Within the framework of the fourth phase of the programme, emphasis is being placed in supporting the ability of developing countries to adapt to climate change. The German programme puts explicit emphasis on the creation of synergies across related activities. Its aim is first to determine the extent to which adaptation measures are already being implemented in ongoing projects, either as targeted measures or as back-up measures in the field of climate protection. In addition, guidelines are under development regarding the integration of such measures into project planning and implementation and the assessment of their impacts. Collaboration with other German development assistance projects—especially those undertaken within the contexts of the Biodiversity and Desertification Conventions—are key priorities.
95.
The Dutch National Climate Assistance Programme (NCAP) is a bilateral assistance programme that aims to assist in the development of activities that can effectively address adaptation to climate change. The programme includes 15 countries and is designed to address adaptation issues in the wider context of poverty alleviation, vulnerable systems and policy development. NCAP projects seek to ensure adequate stakeholder representation, identify a set of climate 21
change adaptation initiatives, establish country-driven criteria by which to evaluate and prioritise adaptation initiatives, make consensus-based recommendations for adaptation activities, and as needed, recommend capacity building and policy, programme and institutional integration, as part of adaptation priority activities. The current phase of the programme is about the urgent actions that developing countries must take to adapt to the negative impacts of climate change (extreme fluctuations in the climate; more frequent and powerful cyclones and hurricanes, more frequent and intense floods and droughts), which are already occurring. Like the German CCAP, the Dutch NCAP explicitly seeks to link activities with any complementary activities taking place, particularly NAPA efforts. 96.
Understanding and exploiting potential synergies between the multilateral and bilateral framework above is critical for promoting technology transfer processes that are effective and efficient. At least three activities—synthesis, networking and innovative financing—will be needed help to facilitate bringing the various facets of technology transfer for adaptation together into a coherent strategy, as outlined below. • Synthesis: As indicated above, there are numerous initiatives, projects, and/or strategies already proposed or in effect, upon which future technology transfer processes could build. They are represented in Action Plans of MEAs and in specific projects undertaken as part of development assistance. A systematic synthesis regarding the types of technology priorities emerging from these activities and which can meet multiple objectives, including climate adaptation, would be helpful in structuring an approach for matching funding with projects that are able to satisfy multiple objectives. The synthesis of appropriate information can facilitate and promote the transfer of technologies for adaptation within and across countries and can help to foster integration with indigenous technologies. • Networking: It would be helpful for networks to be established to facilitate a structured exchange of information regarding various initiatives. At present, the MEAs are implemented independently from each other. With the possible exception of the bilateral programmes described above, this is also largely true of development assistance. A process of developing communication networks amongst Parties involved across the various MEAs and development assistance programmes could help to facilitate the emergence of key lessons, insights and complementarities. • Innovative financing: As has been the case with mitigation, it will be necessary to explore innovative financing mechanisms that can promote, facilitate and support increased investment in technologies for adaptation. At present, most of the attention regarding innovative financing has been devoted to mitigation. Several financing mechanisms have emerged that aim to catalyse change agents, facilitate trading of credits and provide greater overall flexibility for the private sector to invest in mitigation technologies (Van Aalst, 2004). Nothing comparable has thus far emerged for adaptation, where potential technology transfer investments are associated with insufficient incentive regimes, increased risks and high transaction costs. At least two areas would need to be scrutinised to begin the process of developing innovative financing models for adaptation. First, it will be essential clearly to define basic objectives for innovative financing for the transfer of technologies for adaptation. The underlying motivation for these objectives could be to help countries to enhance their adaptive capacity to climate change by helping businesses and the public sector to invest in risk-reducing strategies that capture commercial opportunities. Second, progress will need to made on the dual processes of synthesis and networking activities described above in order to help to educate and link private sector investors, creating stable environments to catalyse investment flows and minimise risk and uncertainty.
5.2. Dimensions of the Transfer of Technologies for Adaptation 97.
Technology transfer processes are complex. Lessons learnt from the overall development process of technology transfer have shown mixed results. For example, computer or mobile phone technologies from industrialised countries have shown almost universal acceptance and 22
penetration in developing countries. But in the cases of many industrial or energy technologies, the results depended on many factors, including skill base at the recipient countries, appropriate market conditions, technology levels and assured supply of services such as electricity and water, appreciation and implementation of quality control, and availability of spare pasts. Often it is a variety of interconnected issues—socio-economic, institutional and governance—that have determined the degree success of technology transfer, rather than the technologies themselves. Hence the assessment of appropriateness of technology in the given context is of utmost importance in the transfer of environmentally sound technologies. 98.
Technology transfer processes between and amongst industrialised and developing countries can have several dimensions. Some of the possible permutations include flows of technology from industrialised to developing countries (and vice versa) and from developing countries to developing countries. Three-way technology flows are also possible between industrialised and groups of developing countries. Appropriate institutional setting and roles of key stakeholders are of primary importance.
99.
There are several stages to co-operation or transfer of environmentally sound technologies. These include technology innovation and development, technology transfer and adaptation, technology diffusion, marketing and acceptance to ensure wide-ranging replication (Metz et al., 2000). A community, enterprise or institution can successfully participate in technology transfer for adaptation if the technologies are appropriate to the needs of the key stakeholders, are financially viable or adequately supported, are part of adaptation strategies that are complementary to their development process, benefits to stakeholders are evident and the system is well-monitored. Hence, technology transfer for adaptation has to be assessed, guided, monitored and embedded in the development process.
100. Governments can create incentives for the transfer of technologies for adaptation by improving national information systems to disseminate information on such technologies, and by expanding credit and savings schemes to assist farmers and other communities to manage increasing climate variability in their environment. Establishing the use of financial incentives and disincentives are government actions that can promote their transfer. 101.
Much attention has been focused in recent years on measures to remove barriers facing the transfer of mitigation technologies that can be integrated in sustainable development strategies. Barriers include limited financing, limited institutional capacity, jurisdictional complexity and the need for community involvement. Each of these barriers applies to some extent to technologies for adaptation. In addition, the transfer of technologies for adaptation faces other barriers, including the additional institutional complexity associated with an expanded stakeholder community and the prevailing reluctance to commit funding to adaptation.
102. Creating enabling environments (i.e., building and strengthening of capacity, especially on a national scale) for the transfer and application of technologies for adaptation is critical. Many such activities will need to be initiated by government agencies, whilst the beneficiaries will likely be the private sector and an assortment of community groups. Aspects of enabling environments are varied but will likely need to include training, local adaptation assessments and different types of information exchanges.
5.3. Integrating Technology Transfer for Adaptation and Development 103. Although climate change is likely to have significant impacts on sectors such agriculture, water, human settlement and health, biodiversity and infrastructure, it is difficult to make climate change as central and urgent in the political decision-making process in most countries. This is a reflection of the difference in timescales between climate change and the immediate demands of most developing countries. 104. The adverse impacts of climate change will fall disproportionately on the most vulnerable in the least developed and developing countries. This implies that poverty alleviation—a primary goal for many countries—as well as the pace of development could be adversely affected due to climate change (Sterling, 2003). “Most analysts in the less-developed countries believe that the 23
urgent need, in the face of both climate variation and prospective climate change, is to identify policies which reduce recurrent vulnerability and increase resilience. Prescriptions for reducing vulnerability span drought-proofing the economy, stimulating economic diversification, adjusting land and water uses, providing social support for dependent populations, and providing financial instruments that spread the risk of adverse consequences from individual to society and over longer periods. For the near term, development strategies should ensure that livelihoods are resilient to a wide range of perturbations.” (Rayner and Malone, 1998). 105. Most countries have experiences with coping with climate variability and have adopted different technologies to reduce impacts of extreme events such as floods, droughts and cyclones. Integrating technologies for adaptation into development plans and programmes is necessary to promote sustainable development and to avoid maladaptation in the long run. To facilitate such integration, a process is necessary to identify possible areas for technology development and transfer, taking into consideration development priorities, the vulnerability of priority sectors and possible measures to address vulnerability. It is anticipated that in the least-developed countries, NAPAs will identify projects that are action-oriented, complementary to and building upon existing plans and programmes, promote sustainable development, consider sound development and environmental practices, and are cost-effective.
6.
CONCLUSIONS AND WORKSHOP DISCUSSION POINTS
106. This background paper has sought to provide a summary overview of the current understanding of adaptation to climate change, the availability and applicability of environmentally sound technologies for adaptation, and the potential to develop and transfer such technologies. It is hoped that it can serve as a useful starting point for a more comprehensive technical paper on the development and transfer of environmentally sound technologies for adaptation to climate change. 107.
This background paper has argued that it is now well recognised that climate change poses a threat to important development issues such as water supply, food security, human health, natural resources and protection against natural hazards. This recognition has moved adaptation to an activity that is considered crucial within the broader context of sustainable development. The link between adaptation and sustainable development has been emphasised as particularly relevant when seeking to enhance the capacity of countries and communities to adapt to climate change, which is often limited by lack of resources, poor institutions and inadequate infrastructure, amongst other things.
108. Several key conclusions emerge from the background paper. First and foremost, technology is not a panacea. Adaptation involves more than merely the application of a particular technology. Adaptation to climate change is an ongoing and reiterative process that includes information development, awareness raising, planning, design, implementation and monitoring. Whilst involving technology, adaptation also requires attention to issues such as private sector engagement, removing barriers to information availability, creating enabling institutional contexts, and the promotion of innovative and flexible financing instruments. 109. Second, reducing vulnerability requires not only having access to technology, but also having the mechanisms, expertise and other resources that are needed to make the technology useable and sustainable. The mere existence of technologies for adaptation does not mean that every vulnerable community, sector or country has access to these options or is in a position to implement them. This highlights the need for technology transfer and capacity building for adaptation. 110.
Third, technologies for adaptation include both hard and soft technologies. Hard technologies for adaptation include drought-resistant seeds, seawalls and irrigation technology, whilst soft technologies for adaptation include insurance schemes, crop rotation patterns and set-back zones, as well as information and knowledge. In practice, a successful adaptation strategy will
24
often combine the application of both hard and soft technologies. Technology transfer for adaptation will therefore have to focus on both types of technology. 111.
Fourth, the range and dimensions of technologies for adaptation that can be considered is very large, as illustrated in this paper by the example of coastal zones. There are many examples of technologies that can be used to collect data, provide information and increase awareness for coastal adaptation to climate change, to plan and design adaptation strategies, to implement adaptation strategies and to monitor and evaluate their performance. Similar lists and descriptions will be useful for considering technologies for adaptation in other vulnerable systems and sectors.
112.
Finally, the transfer of technologies for adaptation is a complex one that involves multiple stakeholders, a variety of perspectives and is highly interdisciplinary. This paper argues that for environmentally sound technologies for adaptation, the process of technology transfer should exploit opportunities represented in various multilateral and bilateral frameworks, taking into account the various dimensions for promoting the transfer of technologies for adaptation and making the overall process more integrated in national development processes.
113.
In closing, it is important to note that this background paper is not intended to impose or prescribe a new framework for technology transfer to the UNFCCC. However, the background paper suggests several issues and questions for consideration. These issues and questions could be a starting point for discussion at the UNFCCC Seminar in Tobago, as well as for the technical paper that is to follow this background paper. Such discussions could assist in identifying how the UNFCCC process could direct its efforts regarding the transfer of technologies for adaptation. Specifically, the following issues could benefit from more detailed discussion: • The distinction between hard and soft technologies. A focus on hard technologies alone is unlikely to be sufficient to address the emerging risks of climate change and implement effective responses for adapting to climate change. Strategic planning for technology transfer should embrace an expansive definition of technology in order to present policymakers with robust choices. • Simplified framework or alternative frameworks. The current presumption, as reflected in this background paper, is that the proposed four-step simplified decision framework could be used in future evaluation processes for selecting and transferring technologies for adaptation. Other frameworks could be used, each with its own unique vocabulary, definitions and specialised tools. Policymakers charged with managing technologies for reducing climate risks almost certainly require that the framework used be at the same time highly focused, sufficiently flexible and amenable to a broad range of national planning contexts. • Innovative financing versus conventional financing. Potential investments in the transfer of technologies for adaptation are currently burdened with insufficient incentive regimes, increased risks and high transaction costs. These factors provide major hurdles for access to financing, lead to high costs of financing, undermine confidence in the process and are becoming increasingly crucial issues, especially when one takes into account declining trends in official development assistance. With limited resources available and competing development priorities, serious efforts need to be devoted to the development of an innovative, creative approach for financing technology transfer for adaptation. The two-step process proposed in this background paper represents an initial effort towards this end. • Sectoral versus livelihoods approach. The challenge in transferring technologies for adaptation begins with an understanding of current vulnerability and the multiple stresses that affect communities, livelihoods, ecosystems and economic sectors. An approach to technology transfer that focuses exclusively on economic sectors may be insufficient to understanding the emerging risks. For instance, the NAPA approach links rapid assessment of adaptation priorities with multi-criteria evaluation of urgent options that are focused on communities and groups that are the most vulnerable to climate change. Strategic thinking about the proper focus for transferring technologies for adaptation may be needed to ensure that the needs of the most vulnerable are prioritised. 25
REFERENCES Arnell, N., 2000: Flood insurance. In: D.J. Parker (ed.), Floods. Volume 1, Routledge, London, UK, pp. 412–424. Baker, T.F., 1993: Absolute sea level measurements, climate change and vertical crustal movements. Global and Planetary Change, 8(3), 149–159. Basher, R.E., 1999: Data requirements for developing adaptations to climate variability and change. Mitigation and Adaptation Strategies for Global Change, 4(3–4), 227–237. Beets, D.J., L. van der Valk and M.J.F. Stive, 1992: Holocene evolution of the coast of Holland. Marine Geology, 103(1–3), 423–443. Bijlsma, L., C.N. Ehler, R.J.T. Klein, S.M. Kulshrestha, R.F. McLean, N. Mimura, R.J. Nicholls, L.A. Nurse, H. Pérez Nieto, E.Z. Stakhiv, R.K. Turner and R.A. Warrick, 1996: Coastal zones and small islands. In Climate Change 1995—Impacts, Adaptations and Mitigation of Climate Change: Scientific-Technical Analyses. Contribution of Working Group II to the Second Assessment Report of the Intergovernmental Panel on Climate Change, R.T.Watson, M.C. Zinyowera, R.H. Moss, (eds.), Cambridge University Press, Cambridge, UK, pp. 289–324. Birkemeier, W.A., H.C. Miller, S.D. Wilhelm, A.E. DeWall and C.S. Gorbics, 1985: A User’s Guide to the Coastal Engineering Research Center’s (CERC’s) Field Research Facility. Instruction report CERC-85-1. U.S. Army Corps of Engineers, Waterways Experiment Station, Vicksburgh, MI, 121 pp. Birkemeier, W.A., R.J. Nicholls and G.-H. Lee, 1999: Storm groups and morphologic change in the nearshore. In: C.N. Kraus and G.W. McDougal (eds.), Coastal Sediments ’99. Proceedings of the 4th International Symposium on Coastal Engineering and Science of Coastal Sediment Processes, Hauppauge, Long Island, NY, 21–23 June 1999, American Society of Civil Engineers, New York, NY, pp. 1109–1122. Boesch, D.F., M.N. Josselyn, A.J. Mehta, J.T. Morris, W.K. Nuttle, C.A. Simenstad and D.J.P. Swift, 1994: Scientific assessment of coastal wetland loss, restoration and management in Louisiana. Journal of Coastal Research, 20, Special Issue, v+103 pp. Burd, F., 1995: Managed Retreat—A Practical Guide. English Nature, Peterborough, UK, 27 pp. Burton, I. and M. van Aalst, 2004: Look before You Leap: A Risk Management Approach for Incorporating Climate Change Adaptation in World Bank Operations. World Bank, Washington, DC, USA, 60 pp. Burton, I., S. Huq, B. Lim, O. Pilifosova and E.L. Schipper, 2002: From impacts assessment to adaptation priorities: the shaping of adaptation policy. Climate Policy, 2(2–3), 145–159. Capobianco, M., 1999: Role and Use of Technologies in Relation to Integrated Coastal Zone Management. Report to the European Union Demonstration Programme on Integrated Coastal Zone Management, Tecnomare S.p.A., Venice, x+106 pp. + apps. Carter, T.R., M.L. Parry, S. Nishioka and H. Harasawa (eds.), 1994: Technical Guidelines for Assessing Climate Change Impacts and Adaptations. Report of Working Group II of the Intergovernmental Panel on Climate Change, University College London and Centre for Global Environmental Research, London, UK and Tsukuba, Japan, x+59 pp. Caton, B. and I. Eliot, 1993: Coastal hazard policy development and the Australian federal system. In Vulnerability Assessment to Sea-Level Rise and Coastal Zone Management. Proceedings of the IPCC/WCC’93 Eastern Hemisphere workshop, Tsukuba, Japan, 3–6 August 1993, R.F. McLean, N. Mimura, (eds.), Department of Environment, Sport and Territories, Canberra, Australia, pp. 417–427. Cazenave, A., K. Dominh, M.C. Gennero and B. Ferret, 1998: Global mean sea level changes observed by TOPEXPOSEIDON and ERS-1. Physics and Chemistry of the Earth, 23(9–10), 1069–1075. Clark, M., 1998: Flood insurance as a management strategy for UK coastal resilience. The Geographical Journal, 164(3), 333–343. Clark, C.D., H.T. Ripley, E.P. Green, A.J. Edwards and P.J. Mumby, 1997: Mapping and measurement of tropical coastal environments with hyperspectral and high spatial resolution data. International Journal of Remote Sensing, 18(2), 237–242. Crichton, D. and C. Mounsey, 1997: How the insurance market will use its flood research. In Proceedings of the 32nd MAFF Conference on Coastal and River Engineering, Keele, UK, 2–4 July 1997, Ministry of Agriculture, Fisheries and Food, London, pp. J31–J34. Crowell, M., S.P. Leatherman and M.K. Buckley, 1991: Historical shoreline change: error analysis and mapping accuracy. Journal of Coastal Research, 7(3), 839–852. Crowell, M., S.P. Leatherman and M.K. Buckley, 1993: Erosion rate analysis: long-term versus short-term data. Shore and Beach, 61(1), 13–20. Davison, A.T., 1993: The national flood insurance program and coastal hazards. In Coastal Zone ’93. Proceedings of the eighth symposium on coastal and ocean management, O.T. Magoon, W.S. Wilson, H. Converse, L.T. Tobin, (eds.), New Orleans, LA, 19–23 July 1993, American Society of Civil Engineers, New York, NY, pp. 1377–1391. Davison, A.T., R.J. Nicholls and S.P. Leatherman, 1992: Beach nourishment as a coastal management tool: an annotated bibliography on developments associated with the artificial nourishment of beaches. Journal of Coastal Research, 8(4), 984–1022. Debusschere, K., S. Penland, K.A. Westphal, P.D. Reimer and R.A. McBride, 1991: Aerial videotape mapping of coastal geomorphic changes. In Coastal Zone ’91. Proceedings of the seventh symposium on coastal and ocean management, Long Beach, CA, 8–12 July 1991, O.T. Magoon, H. Converse, V. Tippie, L.T. Tobin, D. Clark, (eds.), American Society of Civil Engineers, New York, NY, pp. 370–390. Delft Hydraulics and Rijkswaterstaat, 1987: Manual on Artificial Beach Nourishment. CUR Report No. 130. Centre for Civil Engineering Research, Codes and Specifications, Gouda, The Netherlands, 195 pp.
26
Dessai, S. and M. Hulme, 2001: Climatic implications of revised IPCC emission scenarios, the Kyoto Protocol and quantification of uncertainties. Integrated Assessment, 2(3), 159–170. (DETR) Department of the Environment, Transport and the Regions, 2000: Planning Policy Guidance: Development and Flood Risk. Consultation paper, Department of the Environment, Transport and the Regions, London, UK, 51 pp. Doody, P. (ed.), 1985: Sand Dunes and their Management. Nature Conservancy Council, Peterborough, UK, 262 pp. Douglas, B.C., 1991: Global sea-level rise. Journal of Geophysical Research—Oceans, 96(C4), 6981–6992. Emery, K.O. and D.G. Aubrey, 1991: Sea Levels, Land Levels, and Tide Gauges. Springer-Verlag, New York, NY, 237 pp. Engelen, G., R. White and I. Uljee, 1993: Exploratory modelling of socio-economic impacts of climate change. In Climatic Change in the Intra-Americas Sea—Implications of Future Climate on the Ecosystems and SocioEconomic Structure in the Marine and Coastal Regions of the Caribbean Sea, Gulf of Mexico, Bahamas, and the Northeast Coast of South America. G.A. Maul, (ed.), Edward Arnold, London, pp. 350–368. English Nature, 1997: Coastal Zone Conservation. English Nature, Peterborough, 20 pp. (FEMA) Federal Emergency Management Agency, 1986: Coastal Construction Manual. FEMA-55, Federal Emergency Management Agency, Washington, DC, xxi+114 pp. + apps. (FEMA) Federal Emergency Management Agency, 1994: Mitigation of Flood and Erosion Damage to Residential Buildings in Coastal Areas. FEMA-257, Mitigation Directorate, Federal Emergency Management Agency, Washington, DC, ii+34 pp. (FEMA) Federal Emergency Management Agency, 1997: Building Performance Assessment: Hurricane Fran in North Carolina—Observations, Recommendations and Technical Guidance. FEMA-290, Mitigation Directorate, Federal Emergency Management Agency, Washington, DC, viii+60 pp. + apps. French, P.W., 1997: Coastal and Estuarine Management. Routledge, London, xv+251 pp. French, P.W., 1999: Managed retreat: a natural analogue from the Medway estuary, UK. Ocean & Coastal Management, 42(1), 49–62. Fu, L.-L., C.J. Koblinsky, J.-F. Minster and J. Picaut, 1996: Reflecting on the first three years of TOPEX/POSEIDON. Eos Transactions, 77(12), 109,111,117. Gilbert, S. and R. Horner, 1984: The Thames Barrier. Thomas Telford, London, 182 pp. Gorman, L., A. Morang and R. Larson, 1998: Monitoring the coastal environment; part IV: mapping, shoreline changes, and bathymetric analysis. Journal of Coastal Research, 14(1), 61–92. Gornitz, V.M., R.C. Daniels, T.W. White and K.R. Birdwell, 1994: The development of a coastal risk database: vulnerability to sea-level rise in the U.S. Southeast. Journal of Coastal Research, 12, Special Issue, 327– 338. Gröger, M. and H.-P. Plag, 1993: Estimations of a global sea level trend: limitations from the structure of the PSMSL global sea level data set. Global and Planetary Change, 8(3), 161–179. Gross, R., B. Dougherty and K. Kumarsingh, 2004: Conducting Technology Needs Assessments for Climate Change. National Communications Support Unit Handbook, United Nations Development Programme, New York, NY, USA, vi+25 pp. Hamm, L., H. Hanson, M. Capobianco, H.H. Dette, A. Lechuga and R. Spanhoff, 1999: Beach fills in Europe— projects, practises and objectives. In: B. Edge (ed.), Coastal Engineering 1998. Proceedings of the 26th International Coastal Engineering Conference, Copenhagen, Denmark, 22–26 June 1998, American Society of Civil Engineers, New York, NY, pp. 3060–3073. Handmer, J. (ed.), 1997: Flood Warning: Issues and Practice in Total System Design. Flood Hazard Research Centre, Middlesex University, London, UK, 199 pp. Haque, C.E., 1995: Climatic hazards warning process in Bangladesh: experience of and lessons from the 1991 April cyclone. Environmental Management, 19(5), 719–734. Haque, C.E., 1997: Atmospheric hazards preparedness in Bangladesh—a study of warning, adjustments and recovery from the April 1991 cyclone. Natural Hazards, 16(2–3), 181–202. Henderson, F.M., T.F. Hart, Jr., B.P. Heaton and J.E. Portolese, 1999: Mapping coastal ecosystems over a steep development gradient using C-CAP protocols. International Journal of Remote Sensing, 20(4), 727–744. Holman, R.A., A.H. Sallenger Jr., T.C. Lippmann and J.W. Haines, 1994: The application of video image processing to the study of nearshore processes. Oceanography, 6(3), 78–85. Houghton, T., Y. Ding, D.J. Griggs, M. Noguer, P.J. van der Linden, X. Dai, K. Maskell and C.A. Johnson (eds.), 2001: Climate Change 2001—The Scientific Basis. Contribution of Working Group I to the Third Assessment Report of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK, x+881 pp. Hughes, P. and G.B. Brundrit, 1992: An index to assess South Africa’s vulnerability to sea-level rise. South African Journal of Science, 88(6), 308–311. Huq, S. and R.J.T. Klein, 2003: Adaptation to climate change: why and how. SciDev.Net Climate Change Dossier, Policy brief, http://www.scidev.net/dossiers/index.cfm?fuseaction=printarticle&dossier=4&policy=44. IPCC CZMS, 1990: Strategies for Adaptation to Sea Level Rise. Report of the Coastal Zone Management Subgroup, Response Strategies Working Group of the Intergovernmental Panel on Climate Change, Ministry of Transport, Public Works and Water Management, The Hague, x+122 pp. IPCC CZMS, 1992: A common methodology for assessing vulnerability to sea-level rise—second revision. In Global Climate Change and the Rising Challenge of the Sea. Report of the Coastal Zone Management Subgroup, Response Strategies Working Group of the Intergovernmental Panel on Climate Change, Ministry of Transport, Public Works and Water Management, The Hague, Appendix C.
27
Kaly, U.L. and G.P. Jones, 1998: Mangrove restoration: a potential tool for coastal management in tropical developing countries. Ambio, 27(8), 656–661. Kates, R.W., 1997: Climate change 1995—impacts, adaptations, and mitigation. Environment, 39(9), 29–33. Kay, R.C., 1990: Development controls on eroding coastlines—reducing the future impact of greenhouse-induced sea level rise. Land Use Policy, 7(4), 169–172. Kay, R.C. and J.E. Hay, 1993: A decision support approach to coastal vulnerability and resilience assessment: a tool for integrated coastal zone management. In Vulnerability Assessment to Sea-Level Rise and Coastal Zone Management. Proceedings of the IPCC/WCC’93 Eastern Hemisphere workshop, R.F.McLean, N. Mimura, (eds.)Tsukuba, Japan, 3–6 August 1993, Department of Environment, Sport and Territories, Canberra, Australia, pp. 213–225. Kay, R.C., A. Kirkland and I. Stewart, 1996: Planning for future climate change and sea-level rise induced coastal change in Australia and New Zealand. In Greenhouse—Coping with Climate Change. W.J. Bouma, G.I. Pearman, M.R. Manning, (eds.), CSIRO Publishing, Wellington, New Zealand, pp. 377–398. Kelly, M.P., 1991: Global warming: implications for the Thames Barrier and associated defences. In: R. Frassetto (ed.), Impact of Sea Level Rise on Cities and Regions. Proceedings of the 1st International Meeting “Cities on Water”, Venice, Italy, 11–13 December 1989, Marsilio Editori, Venice, Italy, pp. 93–98. Klein, R.J.T., 1998: Towards better understanding, assessment and funding of climate adaptation. Change, 44, 15–19. Klein, R.J.T., E.N. Buckley, J. Aston, R.J. Nicholls, S. Ragoonaden, M. Capobianco, N. Mizutani and P.D. Nunn, 2000: Coastal adaptation. In: Methodological and Technological Issues in Technology Transfer, B. Metz, O.R. Davidson, J.-W. Martens, S.N.M. van Rooijen and L.L. Van Wie McGrory (eds.), Special Report of Working Group III of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK, pp. 349–372. Klein, R.J.T. and R.J. Nicholls, 1998: Coastal zones. In Handbook on Climate Change Impact Assessment and Adaptation Strategies, Version 2.0. J.F.Feenstra, I. Burton, J.B. Smith, R.S.J. Tol, (eds.), United Nations Environment Programme and Institute for Environmental Studies, Vrije Universiteit, Amsterdam and Nairobi, pp. 7.1–7.35. Klein, R.J.T. and R.J. Nicholls, 1999: Assessment of coastal vulnerability to climate change. Ambio, 28(2), 182– 187. Klein, R.J.T., R.J. Nicholls and N. Mimura, 1999: Coastal adaptation to climate change: can the IPCC Technical Guidelines be applied? Mitigation and Adaptation Strategies for Global Change, 4(3–4), 239–252. Klein, R.J.T., R.J. Nicholls, S. Ragoonaden, M. Capobianco, J. Aston and E.N. Buckley, 2001: Technological options for adaptation to climate change in coastal zones. Journal of Coastal Research, 17(3), 531–543. Klein, R.J.T. and R.S.J. Tol, 1997: Adaptation to Climate Change: Options and Technologies—An Overview Paper. Technical Paper FCCC/TP/1997/3, United Nations Framework Convention on Climate Change Secretariat, Bonn, iii+33 pp. Larson, R., A. Morang and L. Gorman, 1997: Monitoring the coastal environment; part II: sediment sampling and geotechnical methods. Journal of Coastal Research, 13(2), 308–330. Leary, N.A., 1999: A framework for benefit-cost analysis of adaptation to climate change and climate variability, Mitigation and Adaptation Strategies for Global Change, 4(3–4), 307–318. Leatherman, S.P., R.J. Nicholls and K.C. Dennis, 1995: Aerial videotape-assisted vulnerability analysis: a costeffective approach to assess sea-level rise impacts. Journal of Coastal Research, 14, Special Issue, 15–25. Leu, L.-G., Y.-Y. Kuo and C.-T. Liu, 1999: Coastal bathymetry from the wave spectrum of SPOT images. Coastal Engineering Journal, 41(1), 21–41. Lillycrop, W.J. and L.L. Estep, 1995: Generational advancements in coastal surveying, mapping. Sea Technology, 36(6), 10–16. Lim, B. and E. Spanger-Siegfried (eds.), 2005: Adaptation Policy Frameworks for Climate Change: Developing Strategies, Policies and Measures. Cambridge University Press, Cambridge, UK, vii+258 pp. Lipton, D.W. and K. Wellman, 1995: Economic Valuation of Natural Resources—A Handbook for Coastal Resource Policymakers. NOAA Coastal Ocean Program Decision Analysis Series No. 5, NOAA Coastal Ocean Office, Silver Spring, MD, viii+131 pp. Martinez-Diaz-De-Leon, A., I.S. Robinson, D. Ballestero and E. Coen, 1999: Wind driven ocean circulation features in the Gulf of Tehuantepec, Mexico, revealed by combined SAR and SST satellite sensor data. International Journal of Remote Sensing, 20(8), 1661–1668. May, P., R.J. Burby, N.J. Ericksen, J.W. Handmer, J.E. Dixon, S. Michaels and D.I. Smith, 1996: Environmental Management and Governance: Intergovernmental Approaches to Hazards and Sustainability. Routledge, London, xvii+254 pp. McCarthy, J.J., O.F. Canziani, N.A. Leary, D.J. Dokken and K.S.White (eds.), 2001: Climate Change 2001: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Third Assessment Report of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK, x+1032 pp. McLean, R., L. Rose, C. Kaluwin and J. Aston (eds.), 1998: The Australia/SPREP Coastal Vulnerability Initiative for Atoll States. Workshop Report, Tarawa, Kiribati, 10–13 February 1997, Environment Australia, Canberra, 26 pp. Metz, B., O.R. Davidson, J.-W. Martens, S.N.M. van Rooijen and L.L. Van Wie McGrory (eds.), 2000: Methodological and Technological Issues in Technology Transfer. Special Report of Working Group III of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK, 466 pp. Miller, L., R. Cheney and J. Lillibridge, 1993: Blending ERS-1 altimetry and tide-gauge data. Eos Transactions, 74(16), 185,197.
28
Mimura, N. and P.D. Nunn, 1998: Trends of beach erosion and shoreline protection in rural Fiji. Journal of Coastal Research, 14(1), 37–46. Moore, L.J., 2000: Shoreline mapping techniques. Journal of Coastal Research, 16(1), 111–124. Morang, A., R. Larson and L. Gorman, 1997a: Monitoring the coastal environment; part I: waves and currents. Journal of Coastal Research, 13(1), 111–133. Morang, A., R. Larson and L. Gorman, 1997b: Monitoring the coastal environment; part III: geophysical and research methods. Journal of Coastal Research, 13(4), 1064–1085. Nakićenović, N. and R. Swart (eds.), 2000: Emissions Scenarios. Special Report of Working Group III of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK, 599 pp. Neilan, R.E., P.A. Van Scoy and P.L. Woodworth (eds.), 1997: Workshop on Methods for Monitoring Sea Level— GPS and Tide Gauge Benchmark Monitoring and GPS Altimeter Calibration. Proceedings of an IGS/PSMSL workshop, Pasadena, CA, 17–18 March 1997, Jet Propulsion Laboratory, California Institute of Technology, Pasadena, CA, xvii+202 pp. Nerem, R.S., 1995: Global mean sea level variation from TOPEX/POSEIDON altimeter data. Science, 268, 708– 710. Nerem, R.S., B.J. Haines, J. Hendricks, J.F. Minster, G.T. Mitchum and W.B. White, 1997: Improved determination of global mean sea level variations using TOPEX/POSEIDON altimeter data. Geophysical Research Letters, 24(11), 1331–1334. Nicholls, R.J. and S.P. Leatherman (eds.), 1995: The potential impact of accelerated sea-level rise on developing countries. Journal of Coastal Research, Special Issue 14, 1–324. Nicholls, R.J. and S.P. Leatherman, 1996: Adapting to sea-level rise: relative sea-level trends to 2100 for the United States. Coastal Management, 24(4), 301–324. (NOAA) National Oceanic and Atmospheric Administration, 1998: International Sea Level Workshop. Workshop Report, Honolulu, HI, 10–11 June 1997, Global Climate Observing System Publ. No. 43, Global Ocean Observing System Publ. No. 55, International CLIVAR Project Office Publ. No. 16, Silver Spring, MD, iv+133 pp. (NRC) National Research Council, 1987: Responding to Changes in Sea Level: Engineering Implications. National Academy Press, Washington, DC, 148 pp. (NRC) National Research Council, 1990: Managing Coastal Erosion. National Academy Press, Washington, DC, 522 pp. (NRC) National Research Council, 1992: Restoration of Aquatic Ecosystems. National Academy Press, Washington, DC, 522 pp. (NRC) National Research Council, 1994: Restoring and Protecting Marine Habitat: The Role of Engineering and Technology. National Academy Press, Washington, DC, 193 pp. Nordstrom, K.F. and S.M. Arens, 1998: The role of human actions in evolution and management of foredunes in The Netherlands and New Jersey. Journal of Coastal Conservation, 4, 169–180. Nordstrom, K.F., R. Lampe and L.M. Vandemark, 1998: Reestablishing naturally functioning dunes on developed coasts. Environmental Management, 25(1), 37–51. Nunn, P.D. and E. Waddell, 1992: Implications of Climate Change and Sea-Level Rise for the Kingdom of Tonga. South Pacific Regional Environment Programme Reports and Studies No. 58, Apia, Samoa, 39 pp. Nunn, P.D., A.D. Ravuvu, W. Aalbersberg, N. Mimura and K. Yamada, 1994a: Assessment of Coastal Vulnerability and Resilience to Sea-Level Rise and Climate Change, Case Study: Yasawa Islands, Fiji— Phase II: Development of Methodology. Environment Agency Japan, Overseas Environment Cooperation Centre Japan, South Pacific Regional Environment Programme, xiv+118 pp. Nunn, P.D., A.D. Ravuvu, E. Balogh, N. Mimura and K. Yamada, 1994b: Assessment of Coastal Vulnerability and Resilience to Sea-Level Rise and Climate Change, Case Study: Savai’i Island, Western Samoa—Phase II: Development of Methodology. Environment Agency Japan, Overseas Environment Cooperation Centre Japan, South Pacific Regional Environment Programme, xiv+109 pp. (OTA) Office of Technology Assessment, 1993: Preparing for an Uncertain Climate, Volume 1.U.S. Congress Publ. No. OTA-O-567, U.S. Government Printing Office, Washington, DC, 359 pp. Owens, S.E. and D.R. Cope, 1992: Land Use Planning Policy and Climate Change. Department of the Environment, Her Majesty’s Stationery Office, London, UK, x+109 pp. Parker, D.J. and J.W. Handmer, 1997: The role of unofficial flood warning systems. Journal of Contingencies and Crisis Management, 6(1), 45–60. Parmesan, C. and G. Yohe, 2003: A globally coherent fingerprint of climate change impacts across natural systems. Nature, 421(6918), 37–42. Parry, M., N. Arnell, M. Hulme, R. Nicholls and M. Livermore, 1998: Adapting to the inevitable, Nature, 395, 741. Penning-Rowsell, E.C. and M. Fordham (eds.), 1994: Floods across Europe—Flood Hazard Assessment, Modelling and Management. Middlesex University Press, London, UK, xviii+214 pp. Penning-Rowsell, E., C.H. Green, P.M. Thompson, A.M. Coker, S.M. Tunstall, C. Richards and D.J. Parker, 1992: The Economics of Coastal Management—A Manual of Benefit Assessment Techniques. Belhaven Press, London, xviii+380 pp. Penning-Rowsell, E., P. Winchester and G. Gardiner, 1998: New approaches to sustainable hazard management for Venice. The Geographical Journal, 164(1), 1–18. Pielke, Jr., R.A. and C.W. Landsea, 1998: Normalized hurricane damages in the United States: 1925–1995. Weather and Forecasting, 13(3), 621–631. Pilarczyk, K.W. (ed.), 1990: Coastal Protection. Proceedings of a short course on coastal protection, Delft, 30 June – 1 July 1990, Balkema, Rotterdam, 500 pp.
29
Pittock, A.B. and R.N. Jones, 2000: Adaptation to what and why? Environmental Monitoring and Assessment, 61(1), 9–35. Plant, N.G. and R.A. Holman, 1997: Intertidal beach profile estimation using video images. Marine Geology, 140(1–2), 1–24. Pope, J., 1997: Responding to coastal erosion and flooding damages. Journal of Coastal Research, 13(3), 704– 710. Pugh, D.T., 1987: Tides, Surges and Mean Sea-Level: A Handbook for Engineers and Scientists. Wiley, Chichester, UK, 472 pp. Rayner, S. and E.L. Malone (eds.), 1998: Human Choice and Climate Change. Battelle Press, Columbus, OH, USA, four volumes. Redfern, H. and R.G. Williams, 1996: Remote sensing—latest developments and uses. Journal of the Institution of Water and Environmental Management, 10(6), 423–428. Ribeiro, J.F., 1996: Desalination Technology—Survey and Prospects. European Commission Joint Research Centre Publ. No. EUR 16434 EN, Institute for Prospective Technological Studies, Seville, vii+56 pp. Rogers, S.M., 1993: Relocating erosion-threatened buildings: a study of North Carolina housemoving. In Coastal Zone ’93. Proceedings of the eighth symposium on coastal and ocean management, O.T. Magoon, W.S. Wilson, H. Converse, L.T. Tobin, (eds.), New Orleans, LA, 19–23 July 1993, American Society of Civil Engineers, New York, NY, pp. 1392–1405. Root, T.L., J.T. Price, K.R. Hall, S.H. Schneider, C. Rosenzweig and J.A. Pounds, 2003: Fingerprints of global warming on wild animals and plants. Nature, 421(6918), 57–60. Rosenthal, U. and P. ’t Hart (eds.), 1998: Flood Response and Crisis Management in Western Europe: A Comparative Analysis. Springer-Verlag, Berlin, 236 pp. Ruth, M. and F. Pieper, 1994: Modeling spatial dynamics of sea-level rise in a coastal area. System Dynamics Review, 10(4), 375–389. Sallenger, A.H., Jr., W. Krabill, J. Brock, R. Swift, M. Jansen, S. Manizade, B. Richmond, M. Hampton and D. Eslinger, 1999: Airborne laser study quantifies El Niño-induced coastal change. Eos Transactions, 80(8), 89,92–93. Shaw, J., R.B. Taylor, D.L. Forbes, M.-H. Ruz and S. Solomon, 1998: Sensitivity of the Coasts of Canada to SeaLevel Rise. Bulletin 505, Geological Survey of Canada, Ottawa, Canada, 79 pp. Silvester, R. and J.R.C. Hsu, 1993: Coastal Stabilization—Innovative Concepts. Prentice Hall, Englewood Cliffs, NJ, 578 pp. Smit, B., I. Burton, R.J.T. Klein and J. Wandel, 2000: An anatomy of adaptation to climate change and variability. Climatic Change, 45(1), 223–251. Smit, B., O. Pilifosova, I. Burton, B. Challenger, S. Huq, R.J.T. Klein and G. Yohe, 2001: Adaptation to climate change in the context of sustainable development and equity. In: Climate Change 2001—Impacts, Adaptation and Vulnerability, J.J. McCarthy, O.F. Canziani, N. Leary, D.J. Dokken and K.S.White (eds.), Contribution of Working Group II to the Third Assessment Report of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK, pp. 877–912. Smith, J.B., R.J.T. Klein and S. Huq, 2003: Climate Change, Adaptive Capacity and Development. Imperial College Press, London, UK, viii+347 pp. Sorensen, R.M., R.N. Weisman and G.P. Lennon, 1984: Control of erosion, inundation and salinity intrusion caused by sea-level rise. In Greenhouse Effect and Sea Level Rise. M.C. Barth, J.G. Titus, (eds.), Van Nostrand Reinhold, New York, NY, pp. 179–214. Stauble, D.K. and W.G. Grosskopf, 1993: Monitoring project response to storms: Ocean City, Maryland beachfill. Shore and Beach, 61(1), 23–33. Stauble, D.K. and N.C. Kraus, 1993: Beach Nourishment Engineering and Management Considerations. American Society of Civil Engineers, New York, NY, 245 pp. Taiepa, T., P. Lyver, P. Horsley, J. Davis, M. Bragg and H. Moller, 1997: Co-management of New Zealand’s conservation estate by Maori and Pakeha—a review. Environmental Conservation, 24(3), 236–250. Titus, J.G., 1991: Greenhouse effect and coastal wetland policy: how Americans could abandon an area the size of Massachusetts at minimum cost. Environmental Management, 15(1), 39–58. Titus, J.G., 1998: Rising seas, coastal erosion and the takings clause: how to save wetlands and beaches without hurting property owners. Maryland Law Review, 57(4), 1279–1399. Titus, J.G., C.Y. Kuo, M.J. Gibbs, T.B. LaRoche, M.K. Webb and J.O. Waddell, 1987: Greenhouse effect, sea level rise and coastal drainage systems. Journal of Water Resources Planning and Management, 113(2), 216– 227. Tri, N.H., W.N. Adger and P.M. Kelly, 1998: Natural resource management in mitigating climate impacts: the example of mangrove restoration in Vietnam. Global Environmental Change, 8(1), 49–61. Tunstall, S.M., 2000: Public perception of environmental changes to the Thames Estuary in London, UK. Journal of Coastal Research, 16(2), 269–277. Tunstall, S.M. and E.C. Penning-Rowsell, 1998: The English beach: experiences and values. The Geographical Journal, 164(3), 319–332. Turner, R.K. and W.N. Adger, 1996: Coastal Zone Resources Assessment Guidelines. Land-Ocean Interactions in the Coastal Zone Reports and Studies No. 4, IGBP/LOICZ, Texel, The Netherlands, iv+101 pp. Van de Plassche, O. (ed.), 1986: Sea Level Research—A Manual for the Collection and Evaluation of Data. Geo Books, Norwich, UK, xxv+618 pp. Vellinga, P., 1986: Beach and Dune Erosion during Storm Surges. PhD thesis, Delft University of Technology, Delft, 169 pp. Verhagen, H.J., 1989: Sand waves along the Dutch coast. Coastal Engineering, 13(2), 129–147.
30
Weiner, C., 1993: Frequency of Tidal Flooding at Boston Harbor. U.S. Army Corps of Engineers, New England Division, Concord, MA, USA. West, J.J. and H. Dowlatabadi, 1999: On assessing the economic impacts of sea-level rise on developed coasts. In Climate, Change and Risk. T.E. Downing, A.A. Olsthoorn, R.S.J. Tol, (eds.), Routledge, London, pp. 205– 220. Wigley, T.M.L., 1998: The Kyoto Protocol: CO2, CH4 and climate implications. Geophysical Research Letters, 25(13), 2285–2288. Wijnberg, K.M. and J.H.J. Terwindt, 1995: Extracting decadal morphological behaviour from high-resolution, long-term bathymetric surveys along the Holland coast using eigenfunction analysis. Marine Geology, 126(1–4), 301–330. Woodworth, P.L., 1991: The Permanent Service for Mean Sea Level and the Global Sea Level Observing System. Journal of Coastal Research, 7(3), 699–710. Yamada, K., P.D. Nunn, N. Mimura, S. Machida and M. Yamamoto, 1995: Methodology for the assessment of vulnerability of South Pacific island countries to sea-level rise and climate change. Journal of Global Environment Engineering, 1(1), 101–125. Zerbini, S., H.-P. Plag, T. Baker, M. Becker, H. Billiris, B. Bürki, H.-G. Kahle, I. Marson, L. Pezzoli, B. Richter, C. Romagnoli, M. Sztobryn, P. Tomasi, M. Tsimplis, G. Veis and G. Verrone, 1996: Sea level in the Mediterranean: a first step towards separating crustal movements and absolute sea-level variations. Global and Planetary Change, 14(1–2), 1–48. Zhang, K., B.C. Douglas and S.P. Leatherman, 1997: East Coast storm surges provide unique climate record. Eos Transactions, 78, 389,396–397.
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Decision 9/CP.5: Development and transfer of technologies: status of the consultative process Decision 4/CP.7: Development and transfer of
Decision 5/CP.4 Implementation of Article 4.8 and 4.9 of the Convention (decision 3/CP.3 and Articles 2.3 and 3.14 of the Kyoto Protocol)
4/CP.4: Development and transfer of technologies
9/CP.3: Development and transfer of technologies
7/CP.2: Development and transfer of technologies
Decision 13/CP.1: Transfer of technology
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Paragraph 4 of the decision requests Annex I Parties of the convention and in particular Annex II Parties: (a) To assist developing country Parties in their efforts to build capacity and institutional frameworks to improve energy efficiency and utilisation of renewable energies through multilateral and bilateral co-operative efforts; (b) To provide assistance to developing country Parties to build capacity for sustainable management, conservation and enhancement, as appropriate, of sinks and reservoirs of all greenhouse gases not controlled by the Montreal Protocol, including biomass, forests and oceans as well as other terrestrial, coastal and marine ecosystems; (c) To assist developing country Parties to build capacity to adapt to the adverse effects of climate change; (d) To assist developing country Parties to strengthen their endogenous capacities and capabilities in the areas of technological and socio-economic research and systematic observation relevant to climate change and its associated adverse effects; (e) Taking into account Article 6 of the Convention, to co-operate in and promote capacity-building of developing country Parties at the international, regional, sub-regional and national levels through co-operation programmes supported by United Nations and other multilateral agencies, as well as bilateral agencies. Decides that the basic elements for further analysis should include the following: (a) Identification of the adverse effects of climate change; (b) Identification of the impacts of the implementation of response measures under the Convention; (c) Identification of the specific needs and concerns of developing country Parties arising from such adverse effects and impacts defined through inter alia the national communications from non-Annex I Parties; (d) Identification and consideration of actions, including actions related to funding, insurance and the transfer of It has also decided to the work programme with 6 actions Invites Parties not included in Annex I to the Convention that have not already done so to report their technology needs, in their national communications, to the extent possible; Urges Parties included in Annex II to the Convention to give particular attention to reporting on technology transfer activities, as specified in part II of the revised guidelines for reporting by Parties included in Annex I to the Convention. Decides to establish an expert group on technology transfer to be nominated by Parties, with the objective of enhancing the implementation of Article 4, paragraph 5, of the Convention, including, inter alia, by analysing and identifying ways to facilitate and advance technology transfer activities and making
Paragraph 3 of the decision requests Annex II parties to the convention (a) To take all practicable steps to promote, facilitate and finance, as appropriate, the transfer of environmentally sound technologies and know-how to developing country Parties and their access thereto; (b) To support capacity-building and the strengthening of appropriate institutions in developing countries to enable the transfer of environmentally sound technologies and know-how;
Paragraph 3 of the decision requested the Subsidiary Body for Implementation to evaluate and report on the transfer of technologies being undertaken between Annex II Parties and other Parties, and to do so by drawing on a roster of experts as referred to above, and to take into account the planned technical report of the Intergovernmental Panel on Climate Change on methodological and technical aspects of technology transfer. Requests the convention secretariat to continue its work on the synthesis and dissemination of information on environmentally sound technologies and knowhow conducive to mitigating, and adapting to, climate change; for example, by accelerating the development of methodologies for adaptation technologies, in particular decision tools to evaluate alternative adaptation strategies, bearing in mind the work programme on methodological issues approved by the Subsidiary Body for Scientific and Technological Advice at its sixth session, which was priority should also be given to methods for evaluating and monitoring the effectiveness and effects of specific policies and measures and for assessing adaptation strategies and technologies. The decision recognised the need for continued efforts by Parties to promote and co-operate in the development, application, diffusion and transfer of technologies. It has also recognised that the private sector plays, in some countries, an important role in the development, transfer and finance of technologies, and that the creation of enabling environments at all levels provides a platform to support the development, use and transfer of environmentally sound technologies and know-how.
Key Features It is decided to provide continuous advice to improve the operational modalities for the effective transfer of technology (4.b); and to support and promote the development of endogenous capacities and appropriate technology relevant to the objectives of the Convention in developing countries which are Parties to the Convention (4.c). Request the Convention Secretariat to give high priority to the development and completion of a survey of the initial technology needs, as well as technology information needs, of Parties not included in Annex I to the Convention (non-Annex I Parties), with a view to providing a progress report to the Subsidiary Body for Scientific and Technological Advice at its fourth session;
ANNEX 1: TECHNOLOGY TRANFER DECISIONS RELATED TO THE UNFCCC
Decision 6/CP.10 Development and transfer of technologies
Decision: 10/CP.8 Development and transfer of technologies Decision: 1/CP.10 Buenos Aires programme of work on adaptation and response measures
Decision 5/CP.7 Implementation of Article 4, paragraphs 8 and 9, of the Convention (decision 3/CP.3 and Article 2, paragraph 3, and Article 3, paragraph 14, of the Kyoto Protocol)
technologies.
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Paragraph 4(b): Vulnerability and Adaptation: decided to (i) carrying out pilot and demonstration projects under decision 5/CP.7, paragraph 7 (b) (v), in particular to take forward adaptation projects identified in national communications and other relevant sources, including activities that strengthen adaptive capacity; (ii) Enhancing technical training for integrated climate change impact and vulnerability assessment across all relevant sectors, and for environmental management relating to climate change under decision 5/CP.7, paragraph 7 (b) (ii); (iii) Promoting the transfer of technologies for adaptation under decision 5/CP.7, paragraph 7 (b) (iv), on an urgent basis in priority sectors, including agriculture and water resources, for example through the exchange of experiences and lessons learned in enhancing resilience to the adverse effects of climate change in key sectors; (iv) Building capacity, including institutional capacity, for preventive measures, planning, preparedness and management of disasters relating to climate change, including contingency planning, in particular for droughts and floods and extreme weather events, in accordance with decision 5/CP.7, paragraphs 7 (b) (vi) and 8 (c). Decides to encourage Parties to explore the opportunity for further joint research and development programmes/projects between Annex II Parties and Parties not included in Annex I to the Convention for the development of environmentally sound technologies to respond to the requirements of Article 4, paragraph 5, of the Convention;
Under vulnerability and adaptation it is decided (iii) Enhancing capacity, including institutional capacity, to integrate adaptation into sustainable development programmes; (iv) Promoting the transfer of adaptation technologies; (v) Establishing pilot or demonstration projects to show how adaptation planning and assessment can be practically translated into projects that will provide real benefits, and may be integrated into national policy and sustainable development planning, on the basis of information provided in the national communications from non-Annex I Parties and/or other relevant sources, and of the staged approach endorsed by the Conference of the Parties in its decision 11/CP.1; (vi) Supporting capacity building, including institutional capacity, for preventive measures, planning, preparedness of disasters relating to climate change, including contingency planning, in particular, for droughts and floods in areas prone to extreme weather events; (vii) Strengthening existing and, where needed, establishing early warning systems for extreme weather events in an integrated and interdisciplinary manner to assist developing country Parties, in particular those most vulnerable to climate change Request SBSTA Chair to conduct consultations and facilitate collaboration among expert groups established under the Convention, to the extent practicable, on their work programmes on crosscutting issues, including those relating to technology transfer and capacity-building activities.
Strengthening existing and, where needed, establishing national and regional centres and institutions for the provision of research, training, education and scientific and technical support in specialised fields relevant to climate change, utilising information technology as much as possible.
recommendations to the Subsidiary Body for Scientific and Technological Advice. See Annex for details Framework for meaningful and effective actions to enhance the implementation of Article 4, paragraph 5, of the Convention Under information and methodologies it is decided strengthening existing and, where needed, establishing national and regional systematic observation and monitoring networks (sea-level rise, climate and hydrological monitoring stations, fire hazards, land degradation, floods, cyclones and droughts);