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Strategies for National Sustainable Development
A Handbook for their Planning and Implementation

Jeremy Carew-Reid. Robert Prescott-Allen,
Stephen Bass and Barry Dalal-Clayton 

Chapter 4
Building a National Sustainable

Development Strategy

Strategies may be international, national, or local, and they may be sectoral or multi-sectoral. This handbook covers national multi-sectoral strategies. In many countries, economic and environmental strategies are unintegrated, each being undertaken parallel to the other. The number of partially integrated strategies is growing as environment strategies address economic and social concerns, and development plans pay more attention to environmental factors. Although integration is increasing, no fully integrated sustainable development strategy yet exists.

A national sustainable development strategy should build on existing strategy initiatives such as a national conservation strategy, environmental action plan or development plan, or a sectoral or subnational strategy. Only in exceptional circumstances will it need to start from scratch.

Conditions required before developing a multi-sectoral national strategy include: a defined need and purpose; a location for the strategy’s steering committee and secretariat where they can have the greatest influence on the national development system; high level support; the commitment of key participants; and a conducive political and social climate.

Necessary conditions that can be generated during the strategy process include: wide understanding of the concepts of sustainable development and the strategy, and of the need for both; clear goals and objectives; a body of well trained, experienced and committed people to drive the strategy; adequate resources; and effective communications.

Many of these conditions can be developed by working on a strategy which is less ambitious than an NSDS, such as a sectoral, regional or local strategy. The feasibility and scope of an NSDS can be determined by assessing whether the conditions can be met (and how to meet them), where change is most needed, how the strategy would relate to the decision-making system, how existing strategy processes can best be enhanced, what resources would be needed, and how they could be provided.  



The main kinds of national strategy

The many different kinds of environment and development strategies may be grouped into six categories, depending on their geographical scope – international, national, or local – and on whether they are devoted to a particular sector or theme or are multi-sectoral (Table 1).

  • International strategies may be global in scope or cover two or more countries grouped politically or by natural region.

  • National strategies focus on a single nation. Various forms of them are described in Box 6. In countries with federal systems, provincial, state or territorial strategies are similar in scope and organization to national strategies.

  • Local or regional strategies cover parts of nations or provinces, the parts being defined politically or administratively (municipalities, counties, regional districts, etc) or naturally (coastal zones, drainage basins, mountain ranges, forests, etc).

At present, most multi-sectoral national strategies have a primary focus on either environment or development. Conservation strategies and environmental action plans cover many environmental and resource management issues, from biodiversity to human settlements. They aim to achieve specific conservation or environmental objectives and to integrate environmental conservation into development.

Conservation strategies and environmental action plans point out the contribution of conservation to development, but seldom deal directly with other aspects of development. They tend to have had their strongest inputs from environmental and natural resource interests, and their inclusion of economic and social interests is usually weaker, employing few techniques for examining economic and social issues.

Development plans cover resource allocation, infrastructure development, public investment, employment generation, and many other aspects of economic development. Economic development tends to be interpreted narrowly, however, and environmental and social concerns are rarely treated in depth. Some development plans explicitly recognize the impact of the plan on the environment and the contribution of environmental resources to the plan’s objectives. But environmental analysis is usually cursory and poorly integrated with economic analysis.

In many countries, economic and environmental strategies are not integrated. Each is undertaken independently, often at a different time, or, at best, in parallel to the other. Development planning and decision-making largely ignore environmental concerns, including the environmental strategy, if one

 
 

Box 6: Various types of national strategy  

Many different strategic approaches have been advocated by governments and international agencies in different contexts. They cover a spectrum, from those that focus mainly on environmental concerns and their integration into the development process — for example, the early National Conservation Strategies (NCSs) — to those that deal with social and economic issues as well; for example, later NCSs and National Environmental Action Plans (NEAPs). Of the approaches listed here, NCSs and NEAPs have provided most of the lessons for all forms of strategy development. Both approaches have had their problems and difficulties as well as successes; but, over time, the lessons learned have led to improvements, with some convergence in approach. National strategies fall into two categories: multi-sectoral; and sectoral or thematic. 

Multi-sectoral strategies  

National Development Plans encompass a wide variety of planning exercises undertaken by national governments, often by the central Ministry of Finance or Development Planning. They are usually for specific periods, and include five-year rolling plans (focusing on increasing productivity or competitiveness, fiscal targets, major infrastructural development, etc); annual budgets; and plans covering human resources, the structure of manufacturing and industry, and public sector enterprises (including investment and privatization). They also include structural adjustment plans negotiated between governments and the International Monetary Fund/World Bank. 

National Conservation Strategies were conceived by IUCN, WWF and UNEP (1980 onwards). These were proposed by the World Conservation Strategy (IUCN/WWF/ UNDP 1980) as the means of providing a comprehensive, cross-sectoral analysis of conservation and resource management issues, to integrate environmental concerns into the development process. They have aimed to identify the country’s most urgent environmental needs, stimulate national debate and raise public consciousness, help decision-makers set priorities and allocate human and financial resources, and build institutional capacity to handle complex environmental issues. NCSs have been strongly process-oriented. Information has been obtained, and analysis undertaken, by cross-sectoral groups. NCSs have sought to develop political consensus around issues identified through such group interaction. Their results include policy documents approved at high level, action plans, and specific programmes and projects. box continues 

National Environmental Action Plans are promoted by the World Bank (1987 onwards) as a condition for receiving loans. These have been undertaken primarily by host country organizations (usually a coordinating ministry) with technical and financial assistance from the World Bank, various international organizations, NGOs and other donors. They have been designed expressly to provide a framework for integrating environmental considerations into a nation’s overall economic and social development programs, sometimes in response to structural adjustment imperatives. They also make recommendations for specific actions, outlining the environmental 
policies, legislation, institutional arrangements, and investment strategies required. They have usually culminated in a package of environmentally-related investment projects, many of which are intended for donor assistance (World Bank 1990, 1991). 

Green Plans, produced to date by Canada and the Netherlands, are an evolving process of comprehensive, national programmes for environmental improvement and resource stewardship, with government-wide objectives and commitments. Key goals include cleaner air, water and soil; protection of ecosystems and species; and contributions to global environmental security. The Netherlands National Environmental Policy Plan is radical. It calls for massive reductions in many emissions and wastes within a generation, backed by major clean-up of contaminated sites, to restore and maintain environmental carrying capacity. Targets and schedules provide a means of gauging success and reinforcing the commitment to environmentally responsible decision-making. 

National Environmental Management Plans are currently being developed by many island countries of the South Pacific, coordinated by the South Pacific Regional Environment Programme (SPREP) with support from the Asian Development Bank, UNDP and IUCN. These plans follow a process of round table discussions and consultation with key decision-makers and organizations. They lead to the definition of a policy framework and portfolio of programmes and projects for donor support. National Sustainable Development Strategies (NSDSs) were called for by Caring for the Earth and Agenda 21. In this handbook, we suggest NSDS as a generic name for a participatory and cyclical process of planning and action to achieve economic, ecological and social objectives in a balanced and integrated manner. NSDSs may take many forms, and incorporate or build on many of the above approaches (EAPs, NCSs, etc.). 

Provincial conservation and sustainable development strategies: in federal countries, provincial (or state) strategies are the equivalent of NCSs and NSDSs in countries with unitary systems. Federal governments may undertake national strategies as well. 

Sectoral or thematic strategies 

Sectoral Master Plans, such as agricultural sector plans and protected area systems plans, are often prepared as a sectoral expression of a five-year development plan, and as a means to coordinate donor involvement in a sector. They have been widely prepared in Asia, sponsored by the Asian Development Bank, for such sectors as forestry, agriculture and tourism. Most are not participatory processes. Several have involved a massive research and policy development effort over many years, and have attempted to address inter-sectoral issues. The plans are a comprehensive information resource, but some bear little relation to the capacity of the sector to implement them. 

Tropical Forestry Action Plans (1986 onwards) are sponsored by FAO and promoted 
under the Tropical Forestry Action Programme (TFAP). These are related to a global strategy developed by FAO, UNDP, the World Bank and World Resources Institute (FAO/WRI/WB/UNDP 1987). National TFAP exercises are undertaken by the country concerned, starting with a multi-sectoral review of forest-related issues, and leading to policy and strategy plans. They are followed by an implementation phase for policies, programmes and projects. The plan seeks to produce informed decisions and action programmes with explicit national targets on policies and practices, afforestation and forest management, forest conservation and restoration, and integration with other sectors. Round tables involving governmental bodies, NGOs, bilateral and multilateral donor agencies, and international organizations are held at different stages of planning and implementation.  

National Plans to Combat Desertification (1985–1988) are sponsored by CILSS (the Permanent Committee for Drought Control in the Sahel). These documents analyze the socio-economic and ecological situation, review current activities and discuss policies and actions required to combat drought; they represent the national anti-desertification plans for a number of Sahelian countries. In addition, national plans are arising out of the international Climate Change Convention and the Biodiversity Convention, and country poverty assessments are planned 
by the World Bank. 

Documents contributing to the strategy processes 

Various country environmental profiles and state-of-the-environment reports are prepared by governments, bilateral aid donors and NGOs. In general, they present information on conditions and trends, identify and analyze causes, links and constraints, and indicate emerging issues and problems. 

UNCED National Reports (1991–1992) on environment and sustainable development are descriptive and analytical documents. They were prepared by national governments, sometimes with NGO involvement. In practice, they varied enormously, but the UNCED Secretariat guidelines proposed that each report should address development trends and environmental impacts and responses to environment and development issues such as principles and goals, policies, legislation, institutions, programmes and projects, and international cooperation. Many countries consulted local, regional and international NGOs and industry. The reports identify how national economic and other activities can stay within the constraints imposed by the need to conserve natural resources. Some consider issues of equity and justice. Certain of them are intended as the foundation for future NSDSs.  

CSD National Reports are designed for reporting to the Commission for Sustainable Development on progress in implementing Agenda 21. Few have been produced to date. 

Note: The 1993 Directory of Country Environmental Studies (WRI/IIED/IUCN 1992) lists, and provides abstracts for, most of the main documents resulting from the above approaches. 


exists. Environmental strategies have been undertaken without sufficient regard for existing planning and decision-making procedures. Some strategies have either duplicated or otherwise failed to coordinate with existing individual sector development plans (such as forestry, agriculture and wildlife). There has often been scant assessment of how the strategy would relate to the development planning system, how to use its strengths, and how to influence it most effectively. One reason for this is the failure to overcome perceptions of the conservation strategy as anti-development or as applying to only a few sectors.

As environmental strategies address economic and social objectives more directly, and development plans pay more attention to environmental objectives, the number of partially integrated strategies is increasing. They include development plans that have not just an environmental chapter, but incorporate environmental considerations in all chapters. They also include conservation strategies and environmental plans that relate directly to the development planning system, and so have begun to make improvements to the development planning process and sectoral decisions.

There are many reasons for this move towards integration:

  • increasing knowledge about development and environment issues and their interactions;

  • the emergence of global environmental and development concerns as key international issues;

  • greater public interest and pressure for change; and

  • the need to define more precise actions, including an environmental investment portfolio.

We know of no example of a fully integrated strategy; one that combines all aspects of social, economic and environmental policy into a sustainable development strategy, as called for by Agenda 21 and Caring for the Earth. The trend is clearly in this direction, however. Sustainable development strategies have the potential to replace the development planning process as we know it today.

The history of national strategies

Placing national strategies for sustainable development in a historical context can help to ease the confusion felt by governments and communities when confronted with the vast array of unrelated strategy options, models and demands on their limited resources.

The momentum for national strategies has built up over the past 30 years. The various approaches have evolved in three broad stages, leading gradually to greater emphasis on local initiative.

  • For some ten years from the early 1970s, effort was concentrated on developing international strategies to tackle specific problems such as population, human settlements and pollution.
  • The 1980s saw the international effort overlaid by a growing interest in more comprehensive strategies at a national level among governments of both north and south. By the end of 1994, more than 100 countries will have embarked upon some form of comprehensive national strategy process; all striving for cross-sectoral relevance and impact.
  • The 1990s have seen an emphasis placed on the need to build capacities to institutionalize and refine these processes with growing attention to the sub-national or local level, for that is where action takes effect. Each level continues to be important in building the global strategic framework for sustainable development.

International efforts to nurture cooperative management of common resources have been limited by the ability of each participating country to act. Governments have accepted a growing range of international obligations and have needed to express these in umbrella national strategies.

A recent example is the Convention on Biodiversity Conservation, which calls for the preparation of national biodiversity strategies. Initially, countries took their lead from the World Conservation Strategy (WCS), published in 1980. The WCS introduced the term ‘sustainable development’ and promoted the preparation of national conservation strategies (NCSs). This concept, based on a process of consensus-building, was the main guiding force in national attempts to reconcile conservation with development for the first half of the 1980s. By 1985, some 30 countries had embarked on a NCS process, largely in isolation from one another but often with assistance from IUCN, which was learning as it went along.


The World Commission on Environment and Development (WCED), which ran from 1985 to 1987, reinforced the value of national strategic approaches and led to a second wave of initiatives. What was becoming apparent during this period was the need for a new, strategic, inter-sectoral approach to managing change; an approach that would overcome the weaknesses of economic planning and piecemeal environment protection policies.

At that time, a number of international organizations came on the scene, with a variety of thematic strategies for selected countries. This greatly complicated the situation. Until then, strategies generally had been the initiatives of governments or national groups, proceeding at a pace and pattern best suited to them. From 1985 on, in response to a global action plan on drought, the United Nations Sudano-Sahelian Office (UNSO) for Africa supported the preparation of national plans to combat desertification. A year later, after the development of a global forestry strategy, the Food and Agricultural Organization (FAO) began sponsoring the preparation of national Tropical Forestry Action Plans (TFAPs). To date, TFAPs have been prepared for 91 countries in all parts of the world. In 1987, the World Bank began helping four countries in Africa prepare National Environment Action Plans (NEAPs). By 1991, ten additional NEAPs had been started. These were in response to an internal World Bank directive, requiring action plans as a Bank loan precondition for the least developed countries. In 1992, this
directive was reinforced and expanded to cover all 110 of the Bank’s borrower countries.


It was appropriate that the next major addition to the strategies family should come with the UN Conference on Environment and Development, otherwise known as the Earth Summit, held in Rio de Janeiro in 1992. The action plan of the conference, Agenda 21, calls on governments to adopt national strategies for sustainable development that ‘build upon and harmonize the various sectoral, social and environmental policies and plans that are operating in the country’. A Capacity 21 programme was
established within UNDP to promote and support the strategies.


The labels in this smorgasbord of strategies – for example, NCSs, TFAPs, NEAPs, NSDSs, Green Plans and NEMPs (National Environment Management Plans in the South Pacific) – imply that each is a distinct entity. In practice, this is not so: there is a great diversity within each type, and overlap among them. Yet one can safely generalize that strategies which have departed from the original model to express true national identity have tended to be the most successful.

Entry points into a multi-sectoral national strategy

It is likely that some kind of strategy on environment and development is being, or has been, undertaken in most countries.
Fresh initiatives should be linked to ongoing or past processes, and be clearly identified as extensions or components of them. NSDSs and other multi-sectoral strategies should build on existing strategic initiatives, not attempt to duplicate or ignore them. Some NEAPs, for example, have ignored established NCSs. Substantial investments have already been made in these existing processes. New investment is likely to be more effective if it draws upon and enhances these processes and does not distract, undermine or devalue them.

The object is not to create a new or separate sustainable development process but to improve existing processes of planning and decision-making. National economic plans, and longer-term strategies such as Malaysia’s Vision 2020, are highly influential because they are linked to powerful economic, industrial and financial ministries. NSDSs should be fully integrated with these plans. Otherwise they risk being marginalized as outside the mainstream of national priorities, and they may be unable to influence the main economic agents of change.

Entry into the kind of multi-sectoral strategy cycle described in this handbook will therefore probably involve one of the following:

  • the further development of an existing multi-sectoral national strategy, such as a National Development Plan, National Conservation Strategy, or Environmental Action Plan;

  • expanding a narrowly-focused initiative, such as a structural adjustment programme;

  • building on a sectoral or thematic strategy or on a multi-sectoral regional or local strategy; and

  • start-up (although this implies starting from scratch, all countries have some form of policy-making and planning process on which to build).

Necessary conditions

The conditions required for an effective multi-sectoral national strategy depend on its scope. The more comprehensive a strategy, the more complex it is. It will require a bigger information base and a wider range of participants. It also demands more money and professional staff with considerably more integration and management skills.

Many difficulties with national strategies have been due to inexperience and lack of appropriate models. Sometimes problems have been severe enough to cause the strategies to lose momentum, reach an impasse on critical issues, lose leadership
and vision, or even be abandoned. In some cases, countries have embarked on multi-sectoral strategies before they were ready for them. The necessary conditions and capacity may need to be developed gradually, through a less ambitious strategy process that, in due course, can be made more comprehensive.

Conditions before developing the strategy

Necessary conditions required before developing a multi-sectoral national strategy include:

1. A defined need and purpose.
The need for a strategy, as the best response to well identified problems, must be evident. It may be that a multi-sectoral national strategy is not an appropriate course of action. A thematic strategy, local strategy, or some more specific action may be better for the time being.

2. A location
for the steering committee and secretariat where they can have the greatest influence on the national evelopment
system. It is impossible to develop and implement a strategy without a clear decision about which organization is directly responsible for it. If the strategy is to be influential, the organization has to be influential.

3. High level support. Political support at a high level – parliamentary, cabinet or head of state – is crucial for the development of a strategy. Support must be visible, and must be based on an understanding of the strategy process and its costs and likely benefits. Since the strategy includes the formulation and implementation of government policy, the highest levels must both support the strategy process and understand its products as they evolve. This support should include:

  • a commitment to develop and implement government policy arising from the strategy, and to commit government funds (and, if necessary, donor assistance) for this purpose;

  • the intention to follow and to consider the policy implications of the strategy throughout the process, and not merely to consider the whole strategy agenda whenever it is formally submitted for adoption;

  • instructions to government departments that their policy formulation and planning should be coordinated with the strategy, unless the topic is outside the scope of the strategy; and

  • the intention to keep the strategy process open and inclusive, and not confidential and closed – encouraging participation in the strategy, giving participants ready access to information, and encouraging them to adopt critical approaches.

4. The commitment of key participants. The participation of certain groups and individuals will depend on the strategy’s scope and purpose. Obviously their participation is essential; if some cannot be induced to participate, this is a sign of inadequate support. A more limited strategy, requiring the involvement of only those who are keen to participate, should be considered, with a view to bringing others on board as the strategy gains in momentum and support.

5. A conducive political and social climate.
Political unrest will make it difficult, if not impossible, to develop a strategy, mainly because the necessary broad consensus cannot be reached. However, the situation shortly after a major political change could provide the right stimulus. Political conditions must be conducive to free speech and participation, giving confidence for creative thinking and a mandate to think critically.

 

Conditions that should be provided while developing the strategy

Necessary conditions that can be generated while developing a strategy include:

1. Wide understanding within the country of the concepts of sustainable development and the strategy; and of the need for both. This can be developed in the course of the strategy, provided a nucleus of key people and organizations are supportive from the outset.

2. Clear objectives
, together with a monitoring mechanism, so that the strategy continues to pursue them and is not diverted or hijacked. The objectives have to be those of the people implementing the strategy, and so must be set in a participatory manner. They can be refined as the strategy progresses.

3. An engine to drive the strategy
, including well-trained and experienced personnel. A body of committed people inside and outside government is needed to drive the strategy throughout, and to provide the main energy source. Capable staff with good management skills and judgement are essential for managing the strategy process. The capacity to manage the process can be developed as part of the strategy.

4. Adequate resources.
Funds have to be available, either from national sources or a combination of national sources and donor funding (see Chapter 10 on donor support). National sources include special allocations of government revenue, adjustments to existing government sectoral budgets and investment plans, the corporate sector, and other participants, such as NGOs. The minimum required is for a steering committee and secretariat to carry out core functions of policy review and development and initial capacity-building activities.

5. Effective communication. Communication is the means by which participants in the strategy:

  • exchange information with each other;

  • reach agreement with each other on actions;

  • undertake actions to change or strengthen values and knowledge; and

  • inform others about the strategy.

Together with participation, communication is the crucial element of the strategy, pervading all others. A communications plan needs to be developed and implemented, covering modes and frequency of communication among participants and between participants and others.

Overcoming obstacles

Several obstacles must be overcome in order to foster the conditions for an effective strategy.

 

Lack of support

A lack of high-level support for a strategy can be overcome by developing awareness and support among interest groups and the public, and by taking every advantage of events that publicize the need for and benefits of a strategy. Many strategies received their initial stimulus from international initiatives, notably the World Conservation Strategy, the report of the WCED (Our Common Future), and UNCED’s Agenda 21. Others have been galvanized by disasters and crises such as the Mount Pinatubo eruption in the Philippines. In Zimbabwe, politicians were influenced to support the development of the national conservation strategy when they were flown to a drought-stricken region and saw for themselves the full extent of land degradation.

 

Lack of capacity

If there is a lack of well-trained personnel, experience or resources, there are several ways to build on, and learn by, experience, using limited resources. One way is to form a team to undertake projects that could eventually contribute to a strategy. Bhutan, for example, has begun by forming a National Environmental Secretariat, with close working ties to the National Planning Commission, whose first task has been to develop an environmental assessment procedure for the country. Another option is to develop either a thematic or a local strategy first. The more modest subject scope of a thematic strategy (covering a single theme such as energy or forestry), and the geographical scope of a local strategy (covering a region or locality), can make them suitable as pilot projects. Through them, the necessary skills can be developed in strategy preparation and implementation, including integrating sectors and managing a complex participatory process. Guinea-Bissau is an example of a small, yet highly diverse country that is developing four local strategies and a regional strategy to gain experience and build the capacity to undertake a national strategy. An advantage of these local strategies is that they cover areas that, ethnically, economically and ecologically, are relatively homogeneous. This makes it easier to find solutions toward sustainable development, although difficulties remain in obtaining the support of national authorities for local development plans. The regional strategy covers half the area of the country and two-thirds of its population. So its problems are similar to those that would be faced by a national strategy, but on a somewhat more manageable scale.

Determining the scope

 

National, local, or sectoral strategies: which comes first?

The variety of national approaches suggests that every answer is potentially correct. Malaysia began with state conservation strategies before embarking on a national conservation strategy, while Pakistan and Zambia developed their national conservation strategy first, and are now developing provincial conservation strategies. Australia’s national conservation strategy led to Victoria’s state conservation strategy, which, in turn, provided a framework for municipal conservation strategies. Several of Canada’s provinces and territories undertook strategies before the federal government; and in some provinces, the first strategies were at the local level. In Cuba, regional multi-sectoral strategies provided crucial experience for the development of a national sectoral strategy (on protected areas). Guatemala has also started regionally (in Petén). Nicaragua began at the national level, but involved all municipalities in developing the strategy. Ethiopia’s national strategy is being elaborated through a set of regional processes. The province of British Columbia has multi-sectoral, sectoral and local
strategies (Box 7).

 

Box 7: Many strategies but no strategy? The case of British Columbia 

The Canadian province of British Columbia illustrates the complex mixture of strategies that can arise as governments respond to different political pressures. The province has several thematic strategies (such as biodiversity and protected areas); two multi-sectoral strategies (the Strategy for Sustainability and the Land Use Strategy) and a number of local strategies. Connections among the strategies are not entirely clear. 

The Strategy for Sustainability is being developed by an advisory body: the Round Table on the Environment and the Economy. It focuses on selected issues: energy, an economic framework, education, and community sustainability. 

The Land Use Strategy is being developed by all groups with an interest in land use (a great many), guided by an independent statutory body: the Commission on Resources and Environment. The strategy is conceived as having three levels: provincial (a framework for the entire province); regional (involving negotiation and allocation of land among the main types of uses); and local (involving detailed management by users, communities and government agencies). Logically, the provincial framework would have been developed first. But allocation of land in regions such as Vancouver Island is politically much more pressing. Consequently, although the strategy is expected eventually to have local and provincial levels, the regional level is being worked on first. 

Several local strategies have been developed, mostly in areas where land use controversies  are particularly heated. Many were initiated before the land use strategy began. 

In short, British Columbia has sectoral and multi-sectoral strategies at local, regional and provincial levels. The scope and level of the strategies has been determined in response to the political needs of the day. This has given each strategy a high degree of political support, at least initially. Also, the number of different strategies at different levels has provided opportunities for a great many different interest groups, agencies and individuals to be involved in the debate on, and movement toward, sustainable development. They have also gained valuable experience in undertaking strategies. 

However, the somewhat confusing and ad hoc array of strategic initiatives, coupled with poorly developed links with other decision-making machinery, has its costs.


Local or regional multi-sectoral strategies and national thematic strategies are valuable for developing experience and building capacities to undertake more complex national strategies. But they are not without problems and are only effective where supported by a suitable national policy framework. Local resource allocation and management decisions taken without reference to national priorities and criteria can result in unacceptable disparities with other areas or simply may be impossible to implement. The success of the Tortuguero Conservation Strategy, a local strategy to control the expansion of banana plantations in Costa Rica, depends not only on actions it is generating at the community level but also on national-level actions.

Local strategies often consist of a mixture of actions undertaken by the participants and recommended actions to be undertaken by higher-level government authorities. Appropriate national policies can define the scope of such recommendations and so ensure that the expectations of the local strategy are realistic. A local strategy in Canada collapsed because of the lack of policies at the provincial level that would have enabled strategy participants to strike an acceptable balance between jobs and protected areas.

There are also risks to undertaking a thematic or sectoral strategy before a multi-sectoral strategy. Sectoral strategies often ignore important inter-sectoral links and impacts. It may prove difficult for an eventual multi-sectoral strategy to harmonize different thematic or sectoral strategies that have been developed in isolation. Ideally, a national multi-sectoral strategy should be developed before local or sectoral strategies, because it can provide a framework for all other strategies whereas local and sectoral strategies cannot. But if it is easier or more effective to develop a local or sectoral strategy first – or if one or the other is necessary to build capacity or support for a national multi-sectoral strategy – then the local or sectoral strategy should come first.

These are key questions that will help to determine whether to undertake a national multi-sectoral strategy, a national sectoral strategy, or a regional or local strategy:

  • Where is the need for change most critical: the nation, a region, a local area, or a sector? Would policies at a higher (eg national) level constrain or foster the possibilities for change at a lower (eg local) level?

  • What organizational/staffing/financial capacity is required for the strategy?

  • What conditions for an effective strategy are missing and how could they be fostered?

  • What can be done with minimal external assistance?

  • The decision-making system and existing strategies

Where does the NSDS fit in the decision-making system and how does it relate to existing initiatives? In practice, almost all countries are already likely to have several multi-sectoral and sectoral strategies or strategy-like initiatives at national, local and intermediate levels. The questions then are:

  • How would the national sustainable development strategy relate to existing planning and decision-making processes? Does it fill a clear niche?

  • What opportunities are there to build on and enhance existing strategy processes and structures? Should the national sustainable development strategy: a) be developed from an existing strategy? If so, which one?; b) start off as a coordinating framework for several existing initiatives, and be developed from there? If so, which strategies and related initiatives most need coordination?; or c) be developed from scratch?

The desirable alternatives are a) or b). Alternative c) would apply only in the unlikely situation of a complete absence of strategic initiatives; if there had been a long gap since the last initiative ceased to play any meaningful role in the country; or if there were unacceptable political costs associated with existing or recent initiatives.

Upgrading an existing strategy

There are several ways of developing one or more existing strategies into a National Sustainable Development Strategy. If there is an economic development plan but no conservation strategy or environmental action plan, then the latter could be prepared, although there is a risk that it would be a poor relation of the development plan. To avoid this:

  • the agencies and planning team responsible for the development plan should be closely involved in the conservation strategy; and

  • the development plan and conservation strategy should be closely linked, with the scope and content of the two corresponding to each other – one providing the socio-economic perspective, the other the socio-environmental perspective (obviously this will entail modifying the development plan, including expanding its scope).

An alternative procedure would be review, modify and expand the development plan so that it provided fully for conservation of ecological processes and biodiversity, protection of natural and cultural heritage, and sustainable use of resources. Similarly, if a conservation strategy or environmental action plan exists but there is no economic development plan (often the case in upper-income countries), then the conservation strategy could be reviewed, modified and expanded to address social and economic objectives. In either case, the logical time for modification and expansion is when the development plan or conservation strategy is due for review. Expanding the scope will involve widening the range of participants in the strategy. Environmental interests and sectors would participate in the development plan; and development sectors and interests would participate in the conservation strategy. Modifications to the existing development plan or conservation strategy might include:

  • Incorporating environmental factors in economic policies, plans and decisions.

  • Developing institutions to integrate social, economic, and environmental objectives.

  • Incorporating environmental components throughout the development plan. Each sector would identify the contribution of environmental goods and services to the sector and the sector’s impact on the environment. The plan would include policies and measures to maintain the environmental goods and services and reduce impacts on the environment. Priority would be given to those areas where environmental goods and services are most at risk or environmental impacts are most severe.

  • Incorporating socio-economic components throughout the conservation strategy or environmental action plan. The strategy would address not merely how to ensure that economic activities are environmentally sound, but how to improve economic performance in ways that are ecologically sustainable and how to improve the quality of life in ways that are economically viable.

The most appropriate course is to combine development and environmental initiatives into one initiative, involving participants in existing multi-sectoral strategies, and building on the processes, institutions, policies and agreements of those strategies. An NSDS could start out as a simple way to coordinate and provide a framework for the often-large number of development and environment initiatives that a country pursues at any one time. These may include a national development plan, national conservation strategy, environmental action plan, forestry action plan, biodiversity strategy, and Agenda 21. Without such a framework, there is a risk of conflict and duplication and of new initiatives diverting attention and resources from the overall process.

 




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