PART C: AIMS AND OBJECTIVES OF DECISION MAKING, TAKING INTO ACCOUNT BIODIVERSITY AND ECOSYSTEM SERVICES
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C.1 Good governance and administrative justice in decision making |
Good governance is especially important in the context of biodiversity because the biophysical environment cannot speak for itself. Thus governments have a responsibility to adopt a long-term view for a nation’s development as the principal custodians of the environment. As noted in Part A.3, southern Africa has a disproportionate fraction of global biodiversity, and it also has a very high direct human dependency on ecosystem services. Thus any decision which affects biodiversity, could also have a long-term effect on the nation’s development and human wellbeing.
C.1.1 Principles of good governance
The term ‘governance’ is a complex and multi-dimensional concept since it incorporates 3 key components[65], namely:
§ A guiding philosophy or core set of agreed operating principles, i.e. public administration must be governed by the democratic values and principles enshrined in a country’s constitution e.g. the right to an environment that is not harmful to health and wellbeing;
§ The preferred ‘process’ that guides the way people interact with each other and with administrative authorities, i.e. the country’s legal framework relating to, for example, the Acts that govern impact assessment, biodiversity and natural resources; and
§ A desired set of ‘products’ or outcomes which are articulated in a country’s hierarchy of conventions, protocols, policies, plans and strategies. For example, by signing the Convention on Biological Diversity the country is accepting a range of obligations to ensure certain outcomes relating to biodiversity management.
So what is ‘good’ governance? The five common principles of good governance are generally accepted to be:[66]
Sustainable development can only be achieved if all sectors of society co-operate and contribute to a common future. That is, it is important that there is strong collaboration between government, science (specialists), and society (including the business sector), as shown in Figure C-1. Decision making must draw on reliable information as well as the values of society and the socio-economic development imperatives of developing nations; impact assessment processes strive to ensure that the ‘trialogue’ between society, decision makers and specialists is adequate.

Figure C-1: Conceptual diagram illustrating the linkages and interfaces between the public, government and science, and their collective contribution to ‘good governance’[67].
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If Interested and Affected persons are not adequately consulted during development planning, they might resort to street protests in an attempt to be heard. Well designed public participation programmes channel energy into constructive dialogue that usually improves project design and implementation. © P. Tarr |
C.1.2 Administrative justice in decision making
Interesting to note:
Environmental conflicts often arise as a result of the incorrect or unjust use of administrative decision making powers.[68]
In most democratic countries, the national constitutions afford citizens the right to administrative action that is lawful, reasonable and procedurally fair. Anyone whose rights have been adversely affected by administrative action has the right to be given a written response for the decision.
So, what are the requirements of lawfulness, procedural fairness and reasonableness?[69]
§ Lawfulness: when the state has a legal duty to act in a certain way and fails to do so, it is acting unlawfully.
§ Procedural fairness: The procedure that the government follows in making an administrative decision must be fair. If there is a set of established rules that the government must follow in coming to the decision, then these must be properly adhered to, including the need to provide written reasons for making the decisions (see Part E.7). The decision can be challenged if the rules are not followed.
Interesting to note: Procedural Fairness Rule
There is one rule that decision makers must always follow, even if there are no other established procedures in place. This rule requires that a person whose rights stand to be affected by an administrative decision, must be allowed to state his or her concerns before the decision is made. Decisions that are made without the affected parties being allowed to state their concerns is thus an unfair decision.
§ Reasonableness: Whether an administrative action is reasonable or not depends on the circumstances surrounding the decision e.g. environmental considerations against which the decision was taken. The questions that a court will ask to test if the decision was reasonable or not are:
o Was the decision the most suitable one to make in the circumstances of the case?
o Was the decision necessary?
o Was the decision proportional? In other words, does it balance the requirements of all the people who will be affected by the decision i.e. the right to administrative or environmental justice.
C.2 Making decisions to achieve sustainable development
Over and above satisfying the principles of good governance and administrative justice in decision making, decision makers must take into account the overarching goal of sustainable development in making decisions.
Interesting to note:
A ‘business as usual’ attitude to decisions that affect the natural environment is making it difficult to change course to a more sustainable development orientated future[70].
Decision making for sustainable development requires critical examination of purposes and alternatives, needs to take into account the applicable regulatory framework, indirect and cumulative, as well as direct and immediate effects, uncertainties and risks, and scientific facts and societal values. It should seek to identify alternatives that offer the greatest overall benefits and avoid undesirable trade-offs, rather than merely enhancing or mitigating the effects of the already chosen options. It also needs an effective means of monitoring effects and enabling adaptive implementation of approved activities.
Interesting to note: Findings of the Situation Assessment, Southern Africa[71]
In the SADC countries, consideration of biodiversity and ecosystem services in decision making is generally inconsistent. Decision makers do not seem to use any explicit decision criteria or criteria for making trade-offs in decision making. Neither the Records of Decision nor the outcome of appeals on Records of Decision reflected any clear rationale. In many instances it seems as if environmental consultants and decision makers are asking different questions of the environmental assessment process.
The problem with current decision making is that it frequently fails to adhere to the principles of sustainable development, due to a number of possible reasons as highlighted in the Situation Assessment:
§ Decision makers’ personal and/or professional opinions often count heavily in decision making.
§ Decision making is often characterized by being ‘short-term and reactive’, ignoring the long-term consequences of irreversible and irreplaceable impacts on ecosystem services. That is, undesirable trade-offs are made between short-term socio-economic gains and long-term impacts on those ecosystem services that support human wellbeing (see Example).
EXAMPLE: UNDESIRABLE TRADE-OFFS, SOUTH AFRICA
Case Study 1: The decision maker on a proposed development noted numerous inconsistencies with spatial planning and land use policy, impacts on the natural environment, the fact that the development changes the predominantly rural and conservation nature of the area, and that the development is not a sustainable land use. In spite of these considerations, the development was authorized on grounds that it would have a desirable socio-economic outcome because there would be benefits to the families residing on the site and nearby. Clearly, the decision did not support the objectives of sustainable development or meet the criteria given in Box C-1. Short term socioeconomic gains were pursued at the expense of significant impacts on both the natural and cultural environment and the social context in the long term, given inconsistencies with strategic planning.
In this instance, no alternative layouts for the proposed development were considered in the EIA. Most of the specialists involved in the EIA recommended that an amended layout plan of the proposed development would avoid or minimize potential negative impacts on biodiversity and ecosystem services, and contribute to an improved proposal. However, the decision maker did not ask for an amended plan.
Case Study 2: A proposed development on the coast was initially turned down since it was in a National Lake Area of possibly international importance, was inconsistent with spatial plans in the area, inconsistent with the coastal zone policy, and was not supported by local authorities.
An appeal on the decision by the proponent resulted in the development being approved. Reasons given were the ‘potential’ for tourism development, foreign investment, and ‘several’ job opportunities, especially during the construction phase. None of these reasons was justified or motivated with facts. Here too, the decision did not support the objectives of sustainable development or meet the criteria given in Box C-1. Short term socioeconomic gains and perceived longer term gains for the economy were pursued at the expense of significant impacts on both the natural environment and the social context in the long term, given inconsistencies with strategic planning and the value of the affected site.
Additional problems with current decision making as highlighted in the Situation Assessment include:
§ Personal bias in decision making is aggravated by impact assessment reports that are biased or give undue emphasis to one or other issue without providing supporting information.
§ The problem of subjective decision making is that many decisions are neither in line with the objectives of sustainable development, nor are they transparent or defensible.
§ Decision making is often inconsistent, leading to loss of credibility of the environmental authority by the public.
§ Changes to the environment as a result of a proposed development are frequently compared to the current situation, rather than to a desired state of the environment. The additive effects of changes are seldom considered.
§ Alternatives are not always required by decision makers or addressed in the impact assessment process, undermining the basis for environmental decision making.
Interesting to note:
In the words of Jared Diamond, the author of “Collapse: How Societies Choose to Fail or Survive”[72], if our society is to succeed, we need:
o The courage to practice long term thinking and to make bold, courageous, anticipatory decisions at a time when problems have become perceptible but before they have reached crisis proportions. This type of thinking “is the opposite of short-term reactive decision-making that too often characterizes our elected politicians”.
The Task Force on Environmental Sustainability of the United Nations Millennium Project [73] echoed this thinking, noting that:
o Achieving environmental sustainability requires dramatic changes in the ways societies and citizens manage biodiversity and the wastes and by-products of human consumption.
Optimum decision making for sustainable development would mean that:
§ Decisions would reflect the realities of the supporting ecological systems, since these systems set constraints and limits on society’s activities. These constraints and limits determine whether or not a society can survive, develop and prosper[74]. Good decision processes will be able to detect threats to systems, identify options to keep systems within safe ranges and allow freedom of choice among the safe decision options according to their present-day goals, values, perceptions and beliefs whilst not jeopardizing future sustainability[75].
§ The comparison of alternatives forms an essential part of making good decisions. Decision making for sustainable development seeks to identify alternatives that offer the greatest overall benefits and avoid undesirable impacts, rather than merely enhancing or mitigating the effects of the already chosen options[76].
§ Decision making would be based on specified goals and desired outcomes, rather than being a comparison with the status quo. Stated simply, if we don’t know where we want to be, we will never get there.
· Decision making would make use of explicit criteria and strive to achieve particular outcomes.
Important to note:
o Increasingly, it is being recognised internationally that explicit criteria for decision making are needed, to provide a clear, transparent and consistent basis for decisions affecting the environment. [77]
o The use of explicit criteria in decision making helps focus the decision maker on internationally and locally accepted objectives for sustainable development, and obligations with regard to, amongst others, biodiversity conservation and the need to strive to achieve the Millennium Development Goals.
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C.3 Criteria and desired outcomes for decision making to support the objectives of sustainable development |

Figure C-2: The Decision Maker’s Dilemma
Box C-1 provides decision criteria and desired outcomes in support of sustainable development.
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Box C-1: Decision criteria and desired outcomes |
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Over-arching criteria and desired outcomes |
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Decisions should: o Try to meet all the requirements for sustainability together as a set of interdependent parts, seeking mutually supportive benefits (e.g. gains in the local economic base will collapse if key ecological functions are not maintained).
Decisions should not: o Accept compromises or trade-offs if they entail further decline, or risks of decline, in officially recognised areas of concern (e.g. official policies, plans, strategies, etc). o Accept any significant long-term loss in any one of the requirements for sustainability. o Accept enhancement of benefits as compensation against incomplete mitigation if stronger mitigation efforts are feasible. o Make compromises or trade-offs where at all possible. Where they are made, they must be explicitly and openly described and justified. o Justify significant negative effects on the integrity of social and ecological systems, or equity and social justice, by compensation through increased economic efficiency (or vice versa). |
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Protecting the integrity and resilience of social and ecological systems |
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Decision criteria |
Desired outcomes |
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Decisions should[91]: o Protect the integrity of social and ecological systems, and the irreplaceable life-support functions on which human and ecological wellbeing depends. o Ensure that livelihoods are maintained or improved. o Favour those actions and options that are most likely to preserve and enhance the opportunities and capabilities of future generations to live sustainably. o Provide and maintain a base for ensuring sustainable livelihoods for all. |
o No net loss of species or ecosystems diversity. o Maintain and conserve natural linkages and corridors between habitats within the same ecosystem, and between ecosystems, along altitudinal and climatic gradients, to allow for ecological and evolutionary processes to continue. o Positive contribution to the conservation of biodiversity and integrity of ecosystems, where at all possible. o The quality and quantity of natural / harvestable goods and ecosystem services, on which the livelihoods and resilience of society in general - and vulnerable communities in particular - depend, should be safeguarded. o Use of natural resources (biodiversity and ecosystem services) should be at or less than rates of replenishment or renewal, or agreed upon thresholds or limits of acceptable change. o Development should avoid the destruction of ecosystems that protect communities from natural hazards. (These ecosystems may not be threatened from a biodiversity perspective but have value and importance by virtue of the protection they afford local communities). |
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Decisions should not: o Accept any significant long term loss. |
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Precaution and adaptation |
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Decision criteria |
Desired outcomes |
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Decisions should: o Respect uncertainty and allow for adaptation. Avoid poorly understood risks of serious or irreversible harm to the foundations of sustainability. Plan to learn, design for surprise and manage for adaptation.
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o Development should have minimal risk of irreversible effects on, or irreplaceable loss of genetic, species or ecosystem diversity. o High level of confidence in predictions as to the effects on biodiversity and ecosystem services. Where confidence levels are low, and / or there are major gaps in information, a risk-averse and precautionary approach should be adopted. o Assurance should be provided that the required mitigation and management of impacts on biodiversity and ecosystem services could - and would - be effectively implemented. |
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Equity and social justice |
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Decision criteria |
Desired outcomes |
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Decisions should: o Reduce the gaps in wellbeing between the wealthy and the poor. o Build democratic governance. o Pursue the benefits of actions that would support both the immediate and long term needs for sustainable development. |
o Decision making should be based on due consideration of all stakeholder values, and should make adequate provision for their access to impact assessment and associated decision processes. o The outcome of development should be an improvement in the fair distribution of rights and access to, management of, and benefits from biodiversity and ecosystem services. o Development should not result in a net cost to society, particularly where the “beneficiaries” of a specific development are single individuals or corporations that derive personal benefit from collective loss. o Development should not result in vulnerable or poor sectors of society having to bear the costs of losing biodiversity or of negative effects on ecosystem services, and any negative effects should not make them increasingly vulnerable or marginalized. o Development should not result in future generations having to bear the costs of lost biodiversity or impaired ecosystem services o Biodiversity and ecosystem services should be preserved for future generations, to optimise their capability of living sustainably. |
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Decisions should not: o Displace significant negative effects from the present to the future.
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Efficiency |
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Decision criteria |
Desired outcomes |
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Decisions should: o Ensure that the net overall effects of development are positive, and choose the development option that promises the greatest long-term gain overall. o Seek to provide a larger base for ensuring sustainable livelihoods for all while reducing threats to the long term integrity of social-ecological systems. |
o Negative effects on the natural environment should not result in a net cost for society, through having to pay to replace or substitute for lost or negatively impacted - and previously free - ecosystem services. o Opportunities and potential benefits lost through a proposed activity should not outweigh gains from that activity. |
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C.4 Co-operative governance at SADC and national levels |
Governments and authorities in SADC countries must ensure that development complies and/or is consistent with a hierarchy of international conventions, regional (NEPAD/SADC) protocols, national and provincial/state laws, policies, plans, programmes and strategies. In most cases, consideration of these conventions, protocols, laws, policies, plans, programmes and strategies requires either co-operation between countries and/or co-operation between different government authorities and agencies.
Box C-2 lists those conventions, agreements, policies and statutes that are of particular relevance to this guidance.
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International conventions o The Convention on Biological Diversity o The Ramsar Convention o The Convention on International Trade in Endangered Species o The Convention on the Conservation of Migratory Species of Wild Animals (Bonn Convention or the CMS) o The UN Convention to Combat Desertification (CCD) Regional protocols o NEPAD and SADC protocols, particularly those related to the Southern Africa Sub-regional Environmental Action Plan of the Environmental Action Plan of NEPAD (currently being revised) o The Protocol on Shared Water Resources o The Protocol on Trade o The Protocol on Mining o The Protocol on the Development of Tourism o The Protocol on Wildlife Conservation and Law Enforcement o The Fisheries Protocol o The Forest Protocol National laws, policies and plans o Impact assessment laws o Spatial development plans and frameworks o Land use plans |
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A number of SADC treaties make provision for cooperative management of resources, especially those with transboundary dimensions. A more innovative approach would be to negotiate the sharing of benefits rather than resources, so as to prevent “national projects” being implemented in places with no comparative advantage. © P.Tarr |
Four African initiatives have emphasised the importance of strong political commitment and good governance in all African countries to ensure that development does not destroy the resource base on which it is based.[83] The central theme that emerged from these meetings was the recognition that sustainable development was essential, but would only be achieved if African countries had sufficient institutional, technological and human capacity. Significantly, it was also recognised that this would require close cooperation from all sectors of government and civil society.
Interesting to note: Findings of the Situation Assessment, Southern Africa[84]
o Projects which had a high degree of inter-departmental co-operation were usually more successful than those which had little or fragmented consultation with relevant line ministries.
o Difficulties arise when the roles and responsibilities of local and national (or provincial) government overlap e.g. in metropolitan areas where there is a lack of adequate consultation between different levels of government.
o Involvement of the biodiversity agency and biodiversity NGOs seem to have had a major beneficial effect on shaping proposals and optimizing decision making. Omission of these bodies from the planning and EIA / SEA process frequently led to the decision being appealed or delayed.
It is essential to ensure co-operation and consultation with other government departments and ministries, both within countries and between neighbouring countries for a number of reasons:
§ Co-operation as early as possible in the planning process allows for shared objectives, outcomes and criteria for both the impact assessment and associated decision making to be determined. In many instances, different countries or jurisdictions have different laws, policies and priorities; the early rationalisation of these different formal requirements and value systems is important to ensure an optimum outcome for sustainable development.
§ Because environmental issues are cross-cutting, most project applications will involve at least one other line ministry.
§ Large-scale infrastructure projects e.g. a national road, may cross provincial or state boundaries and therefore more than one environmental authority may be involved, depending on the administrative structure of the country;
§ Large-scale infrastructure projects may involve more than one country, e.g. transmission lines or any water projects in a shared river basin, and then different national jurisdictions need to be consulted to ensure harmonisation in approach;
§ Projects which are planned in and around an urban area may fall under both national and local authorities.
The checklist in Box C-3 provides an aide mémoire for environmental authorities to ensure that all the correct government stakeholders are consulted at the outset of a planned development.
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Box C-3: Checklist of government departments |
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Local Government* |
Provincial/ National Dept./ Ministries* |
Other Countries |
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o Housing o Water o Sewage o Waste o Roads o Traffic o Town planning o Parks and recreation o Electricity |
o Energy o Mines and mineral resources o Water o Natural resources o Transport o Public works o Health o Trade and Industry o Agriculture o Forestry o Fisheries o Heritage o Conservation, wildlife and parks o Tourism o Town, regional and rural planning o Marine resources |
o Foreign Affairs o All countries affected by proposed laws, policies or plans (e.g. trade) o All downstream countries affected by a river development project o All countries which may be affected by a pollution plume from the proposed project o All countries which may be party to a trans-frontier park or other similar development o All countries involved in inter-basin transfer schemes o All countries affected by power line inter-connectors |
* Generic titles have been given, but each country has its own nomenclature for its government Ministries or Departments.
Some biodiversity agencies may fall directly under line ministries, but in some countries they may form separate parastatal agencies e.g. parks boards, institutes, museums, aquaria, foundations, trusts and societies. These agencies must be contacted at the outset of the impact assessment process and need to be involved in the decision-making process.
Most inter-basin states have set up joint management commissions or authorities e.g. the Zambezi River Authority, which need to be consulted for any project which will affect the flow and quality of water within the affected river catchment.
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It is increasingly common that different government agencies combine their capacity to consider development initiatives. Best practice has shown that the addition of civil society and experts to such fora, considerably improves transparency in decision making processes and increases technical understanding of the issues at hand. © P.Tarr |
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C.5 Deciding on the most appropriate level of assessment – SEA or EIA? |
One of the first and most critical decisions is to determine which level of assessment is appropriate for the application – a strategic environmental assessment (SEA) or an environmental impact assessment (EIA). The following guidance is intended to help with this decision.
C.5.1 Definitions
§ Environmental Impact Assessment (EIA) is the application of impact assessment to individual projects. Typically, EIA is not proactive in its approach, focuses on a specific project and the affected site, and seldom considers landscape scale or cumulative impacts.
§ Strategic Environmental Assessment (SEA) is the application of impact assessment to policies, plans, and programmes. There are many different approaches to SEA, ranging from the ‘EIA’ model where the impact assessment is carried out on a policy, plan or programme once it has already been developed (i.e. reactive), to an integrated and/or ‘sustainability led’ approach that strives to meet sustainable development objectives, is proactive and can be ‘built into’ policy and planning processes. Importantly, impact assessment at strategic level encourages an ‘opportunities and constraints’ type approach to development, where such things as natural resources and ecosystem services at landscape scale define the ‘framework’ within which development can take place and the types of development that could be sustained.
Use Box C-4 to decide whether an SEA or EIA would be the most appropriate tool to assess the impacts of a development proposal, plan, policy or programme.
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Box C-4: Characteristics of SEA and EIA[85] |
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EIA |
SEA |
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Is reactive to a development proposal. |
Is often pro-active and informs development proposals. |
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Assesses the effect of a proposed development on the environment. |
May assess the effect of existing environmental conditions on development needs and opportunities. |
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Relates to a specific project and thus seldom considers cumulative effects. |
Relates to areas, regions or sectors of development and thus has to consider cumulative effects. |
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Has a well-defined beginning and end and focuses on informing a specific decision at a particular point in time. |
May be a continuing process aimed at providing information at the right time. |
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Enables the identification of specific impacts. |
May create a framework against which specific project types can be selected and where impacts and benefits can be measured. |
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Focuses on the mitigation of negative impacts and the enhancement of positive impacts. |
May focus on maintaining a chosen level of environmental quality, e.g. through the identification of sustainability objectives and limits of acceptable change. |
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Has a narrow perspective and includes a high level of detail. |
Has a wide perspective and a low level of detail to provide a vision and overall framework. |
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