South Africa’s conservation system is broader than its formally declared protected areas. Protected areas remain the country’s clearest statutory conservation tool, but biodiversity stewardship agreements, other conservation areas, OECMs, Key Biodiversity Areas, biosphere reserves, Ramsar wetlands, transfrontier conservation areas and marine protected areas serve different purposes. They differ in legal force, tenure, governance, monitoring, community rights and access to finance.
The central rule is simple: a protected area is formally declared or recognized under South Africa’s protected-areas law. An OECM is outside that protected-area category and must demonstrate effective governance, management and positive, sustained in-situ biodiversity outcomes. A KBA identifies importance; it does not itself create legal protection. Stewardship can lead to a protected area, a conservation agreement or another partnership arrangement, but it does not automatically make a site an OECM.
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The essential distinction: designation, agreement and outcome are not the same thing
Area-based conservation labels answer different questions. A legal protected-area designation asks whether land or water has been formally protected under the National Environmental Management: Protected Areas Act 57 of 2003. A stewardship agreement asks how biodiversity-priority landholders, communities and government will cooperate. An OECM asks whether a geographically defined area outside the protected-area system is governed and managed well enough to deliver positive and sustained biodiversity conservation outcomes. A KBA asks whether a place is important for biodiversity, not whether it is protected.
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| Mechanism | What it primarily establishes | Legal position | How it relates to OECMs |
|---|---|---|---|
| Protected area | Formal, place-based legal protection for biodiversity | Declared or recognized under the Protected Areas Act | Excluded from the OECM category |
| Biodiversity stewardship | An agreement-based way to secure priority land and support conservation | Varies by category and agreement; security is not uniform | Some stewardship sites may qualify, but assessment is required |
| OECM | Demonstrated, sustained conservation outcomes outside protected areas | Outcome-based recognition; the 2026 norms source is a draft for comment, not a confirmed final standard | By definition, separate from protected areas |
| Conservation area | A broad description for land managed partly or wholly for conservation | Not one uniform legal status | May be assessed individually |
| Key Biodiversity Area | Evidence that a place is nationally or globally important for biodiversity | Prioritisation concept; no protection is conferred by the label itself | Can be a candidate location, not proof of qualification |
| Biosphere reserve | A landscape approach combining conservation, sustainable use and learning | International programme designation with its own governance arrangements | Does not automatically qualify any zone as an OECM |
| Ramsar wetland | International recognition of a wetland’s importance | Convention-based designation with site-level management obligations and arrangements | Must be assessed against OECM criteria separately |
| Transfrontier conservation area | Cooperation across an international boundary | Component areas retain their own national and local statuses | The overall TFCA is not automatically an OECM |
| Marine protected area | Legal protection for a marine or coastal area | Where declared under the national protected-area framework, it is a protected area | Protected marine areas are excluded; other marine sites may be assessed |
Protected areas: the statutory baseline
The Department of Forestry, Fisheries and the Environment describes protected areas as geographically defined areas formally protected under the National Environmental Management: Protected Areas Act 57 of 2003, primarily for biodiversity conservation. The declaration or recognition creates the strongest and most direct legal basis in this comparison: boundaries, permitted activities, management duties and enforcement are tied to a statutory instrument and the applicable management plan.
That legal durability has advantages. It supports long-term planning, enables restrictions to be enforced and gives public agencies a clear mandate. It can also impose costs: management authorities need staff, budgets, ecological monitoring and lawful processes for access, harvesting, development and benefit sharing. A declaration does not erase existing rights or remove the need to address communities, land claims, local livelihoods and cultural values.
Protected areas are not automatically interchangeable with every other label. A marine protected area may be a protected area in the legal sense when declared under the relevant national framework, while a marine site outside that framework would need a different legal or outcome-based route. Likewise, a protected area inside a transfrontier conservation area remains a protected area even though the wider landscape has a cross-border designation.
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Biodiversity stewardship: agreements that secure priority land
Biodiversity stewardship is a practical mechanism for bringing privately owned land, communal land and community partnership structures into conservation. Instead of relying only on state acquisition or declaration, government and conservation agencies negotiate with landholders and rights-holders in biodiversity-priority areas. The agreement can support ecological management, incentives, technical assistance and, where appropriate, a route toward formal protected-area status.
Stewardship is not a single legal category. The 2021 concept note identifies three broad categories:
Category 1: protected areas
These are stewardship outcomes that become formal protected areas. Once declared or recognized under the Protected Areas Act, they have the statutory status of protected areas and are excluded from the OECM category. The fact that a site originated through a voluntary stewardship process does not weaken its later legal status.
Category 2: conservation areas
This category includes arrangements such as biodiversity agreements and conservation servitudes. They can secure important habitat while allowing specified compatible land uses, but the duration, enforceability, management obligations and legal remedies depend on the instrument and its parties. The concept note identified Category 2 as an initial focus for possible OECM assessment. That was a screening priority, not a declaration that every Category 2 site qualifies.
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Category 3: biodiversity partnership areas
These include conservancies and similar partnership arrangements. They can coordinate landholders and improve landscape management, but participation, funding and ecological outcomes may vary from one partnership to another. A partnership label cannot substitute for evidence that biodiversity outcomes are sustained.
Stewardship therefore answers the question, “How can priority land be secured through cooperation?” It does not answer, by itself, “Is this an OECM?” A site must be examined for governance, management, in-situ results, duration and local values. The same caution applies to communal-land arrangements: community participation is essential, but the existence of a community agreement alone does not prove effective conservation.
What an OECM is in South Africa
The DFFE definition states that an OECM is: “A geographically defined area other than a Protected Area which is governed and managed in ways that achieve positive and sustained long-term outcomes for the in-situ conservation of biodiversity, with associated ecosystem functions and services and where applicable, cultural, spiritual, socio-economic, and other locally relevant values.”
Four elements are decisive:
- It is geographically defined. Boundaries must be identifiable, not merely a general intention to conserve a landscape.
- It is outside the protected-area category. A protected area cannot be counted again as an OECM.
- Governance and management are effective. There must be a responsible authority or arrangement, legitimate decision-making and management that can be implemented.
- Conservation outcomes are positive and sustained. The site must deliver in-situ biodiversity conservation over the long term, alongside ecosystem functions and, where relevant, cultural, spiritual and socioeconomic values.
Conservation does not have to be the site’s primary purpose. A military property, indigenous forest or botanical garden could potentially qualify if its governance and management produce the required outcomes. Conversely, a site managed with conservation as an explicit goal can fail if outcomes are not sustained, governance is ineffective or the area is already a protected area.
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The 2026 OECM norms document describes “long-term outcomes” as outcomes maintained for at least five years. It is expressly an invitation for comment. Unless a later official instrument has been adopted, it should be treated as a draft policy proposal rather than a finalized, binding national standard. The five-year wording is therefore useful for understanding the draft framework, not a licence to claim that every site meeting five years has automatically been recognized.
Potential is not recognition
A DFFE-hosted resource page relays an estimate by Donald and colleagues (2019) that potentially 48.5% of South Africa’s unprotected Key Biodiversity Areas could meet the OECM definition. This is a potential estimate, not the proportion already assessed, reported or recognized as OECMs. It should not be presented as the current national total.
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How stewardship and OECMs overlap without becoming synonyms
Stewardship is one possible pathway to an OECM, but it is not the only pathway. A stewardship agreement may produce a Category 1 protected area, a Category 2 conservation area, a Category 3 partnership area or another arrangement. Only a site-by-site assessment can determine whether a non-protected stewardship site meets OECM criteria.
OECMs can also arise outside stewardship. The concept note points to possible sites on military land, in indigenous forests and in botanical gardens. These examples show why the OECM test focuses on outcomes and governance rather than on the name of the landholder or the original purpose of the property.
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1Repair Windows errors before they cause bigger problems2Scan for outdated or missing drivers - takes under a minute3Clear out junk files and repair common Windows errorsFor landholders, the distinction matters in negotiations and reporting. An agreement may provide valuable conservation security without carrying an OECM designation. For government and funders, it matters because reporting a site as an OECM implies evidence of effective management and sustained outcomes, not merely biodiversity value or a signed memorandum.
Conservation areas: useful umbrella, uneven security
“Conservation area” is often used for land managed to retain or restore biodiversity outside the formal protected-area network. In the stewardship framework, biodiversity agreements and conservation servitudes are examples. Elsewhere, the phrase may describe a local initiative, a private reserve, a conservancy or a landscape project.
Because the term is broad, ask five questions before relying on it:
- What instrument created the area: statute, servitude, contract, management plan or voluntary commitment?
- Who owns or occupies the land, and who has decision-making authority?
- How long do the obligations last, and what happens if ownership or leadership changes?
- Which activities are restricted, permitted or monitored?
- What evidence shows that biodiversity outcomes are positive and sustained?
Without those answers, a conservation-area label says little about enforceability or OECM eligibility. The legal analysis published in 2023 argued that domestic statutory recognition of OECMs was not then established and identified governance gaps affecting conservation areas. That was an analysis of the law at its publication date; the later draft norms indicate policy development but do not, in the material available here, establish that a final binding standard was adopted.
Key Biodiversity Areas: priority evidence, not legal protection
A Key Biodiversity Area identifies a place that is important for biodiversity based on established criteria. It helps governments, conservation organisations and land managers direct attention, planning and finance. It can be a powerful starting point for stewardship or OECM screening.
A KBA does not itself create a protected area, regulate land use or guarantee management. The concept note is explicit that KBAs do not confer formal protection. A KBA may overlap a national park, a private farm, communal land, a military property or no effective conservation arrangement at all. Its significance is the biodiversity evidence; the legal and governance consequences must come from another mechanism.
Biosphere reserves: landscape-scale cooperation and zoning
UNESCO biosphere reserves are landscape approaches that combine biodiversity conservation, sustainable use, research, education and local development. Their governance normally works across zones and multiple land tenures rather than treating the entire reserve as one uniform protected area.
A biosphere reserve can therefore contain statutory protected areas, working farms, settlements, communal land and restoration sites. The designation can improve coordination and make community values, jobs and sustainable use part of the planning conversation. It does not convert every zone into a protected area or an OECM. Each component must retain its own legal status and, if OECM recognition is sought, be assessed separately for governance, management and sustained outcomes.
Ramsar wetlands: international wetland recognition
Ramsar sites are wetlands recognized under the international Ramsar framework. The designation highlights a wetland’s importance and supports conservation and wise-use planning. It can bring visibility, technical attention and a stronger basis for integrating water, biodiversity and livelihood considerations.
Ramsar status is not a substitute for a national protected-area declaration. A Ramsar wetland may overlap a protected area, a stewardship site, a communal landscape or a working production area. Its OECM status cannot be inferred from the Ramsar label; the area, governance arrangement and conservation outcomes must be tested against the OECM criteria.
Transfrontier conservation areas: cooperation across borders
Transfrontier conservation areas, or TFCAs, are cross-border regions where neighbouring countries cooperate on conservation and compatible land uses. The DFFE portal emphasizes that component areas can retain different conservation statuses. One side may contain a national park, another a community-managed landscape, and another private or state land under a different instrument.
The TFCA is therefore a coordination framework, not a single replacement legal status. It can help align wildlife movement, tourism, community development, law enforcement and ecological monitoring across a boundary. It does not make the entire cross-border region an OECM, and it does not erase the domestic laws governing each component.
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Marine protected areas apply the protected-area concept to coastal and ocean spaces. Where a marine area is declared or recognized under the national protected-area framework, it is a protected area and is excluded from OECM classification. Its management can still involve fisheries controls, zoning, research, cultural uses and community interests, but those details arise from the applicable legal instrument and management plan.
Marine conservation also illustrates why location alone is not enough. A locally managed coastal area, a seasonal fisheries closure or a shipping-related restriction might produce biodiversity benefits, but it would need a defined boundary, legitimate governance and evidence of sustained in-situ outcomes before anyone could describe it as an OECM. A marine label or a conservation intention is not automatic recognition.
Governance, tenure and community values
Area-based conservation succeeds or fails through governance as much as through ecological ambition. The relevant questions differ by site:
- Rights and tenure: Who owns, occupies or uses the land or water? Are customary, communal, private, leasehold or access rights documented?
- Consent and representation: Which people must agree, and does the decision-making body genuinely represent affected rights-holders?
- Authority: Who can approve a management plan, enforce rules, resolve disputes and maintain records?
- Duration: Does the arrangement survive a sale, leadership change, budget reduction or political transition?
- Benefits: Are jobs, tourism revenue, restoration income or other livelihood benefits defined and shared fairly?
- Cultural values: Are spiritual sites, customary practices and locally important species included in management decisions?
The DFFE portal stresses community involvement in biosphere reserve, OECM and TFCA programmes and links conservation areas with rural jobs and revenue opportunities. Those are programme rationales, not evidence that every site has delivered equitable benefits. An agreement should specify benefit mechanisms, grievance processes and monitoring rather than assuming that participation automatically produces fairness.
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Conservation effectiveness and monitoring
Legal durability and ecological effectiveness are related but not identical. A protected area can have strong statutory rules yet lack staff or funding. A voluntary agreement can be well managed and ecologically successful but vulnerable to withdrawal or ownership change. OECM assessment requires evidence that management is producing positive and sustained in-situ outcomes.
A credible monitoring system should establish a baseline and track indicators suited to the site, such as habitat condition, population trends, invasive species, fire regimes, water quality or pressure from extraction. It should identify who collects data, how often, what triggers corrective action and where results are reported. Five years of activity under the draft norms is not the same as proof of permanent security; duration, enforcement and future financing still matter.
Monitoring should include ecosystem functions and locally relevant values where applicable. For a wetland, that may include water regulation and culturally important harvesting. For communal rangeland, it may include grazing rules, livelihood use and habitat condition. For a botanical garden, it may include ex-situ collections alongside in-situ habitat management. The indicators must match the actual conservation claim.
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Stewardship can combine public support, external conservation funds, private investment and tax incentives. At a 22 May 2026 speech, Deputy Minister Narend Singh reported approximately R562 million in tax benefits across 24 sites covering 65,760 hectares. He also reported US$64.5 million from multilateral and international funds and R197.5 million from local conservation funds over two decades, describing these as investments enabled by biodiversity stewardship.
These figures are attributed government-reported totals, not a guaranteed return for every agreement. They also do not establish that all sites received equal benefits or that the amounts recur annually. Eligibility, timing and accounting depend on the specific legal instrument and funding programme.
The OECD’s 2025 report describes South African incentives associated with section 37D and section 37C(1), and notes a threatened-species incentive introduced in 2023. It also reports historical results: approximately 500,000 hectares added to the protected-area network through the section 37D incentive and about R189 million in tax deductions recorded in 2020–21 taxpayer returns. Those are historical figures for the periods stated, not current annual performance.
Finance remains a constraint. Deputy Minister Singh said, “Insufficient financial resourcing is one of the key constraints to biodiversity stewardship, despite it being a cost-effective way to support and expand protected areas and job creation.” A conservation agreement should therefore identify the funding needed for patrols, ecological monitoring, administration, community engagement and dispute resolution, rather than relying on the assumption that designation will attract money automatically.
A decision framework for choosing a mechanism
Landowners, communities, conservation agencies and planners can use the following sequence before selecting a label:
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- Define the conservation problem. Identify the species, ecosystem, ecological process or cultural value requiring protection and map the proposed boundary.
- Check existing legal status. Determine whether the site is already a protected area, part of a marine protected area, inside a TFCA or covered by another binding instrument.
- Map rights and governance. Record ownership, occupation, customary rights, community institutions, public authorities and users whose livelihoods may be affected.
- Choose the primary tool. Consider statutory declaration where durable legal protection is needed; stewardship where agreement-based security and incentives are workable; a landscape designation where coordination is the main need; or another sectoral instrument where conservation is an outcome of an existing land use.
- Test OECM eligibility separately. Confirm that the area is outside the protected-area category and document governance, management, sustained in-situ outcomes and relevant ecosystem and local values.
- Build a management and monitoring plan. Set measurable outcomes, responsibilities, reporting dates, adaptive-management triggers and safeguards for rights-holders.
- Secure finance and review clauses. Match costs to realistic public, private or external funding, and state what happens if funding, ownership or participation changes.
- Report the narrowest accurate status. Call a site a KBA, Ramsar wetland, biosphere reserve, TFCA component, stewardship area or conservation area only when that is the established designation. Use OECM terminology only after the relevant assessment and recognition process.
Common mistakes and how to avoid them
Treating every valuable site as an OECM
Biodiversity importance is necessary to conservation planning but is not sufficient for OECM status. Document the governance, management and sustained outcomes test.
Counting protected areas twice
OECMs are outside the protected-area category. A protected area created through stewardship remains a protected area; it should not be reclassified as an OECM for the same conservation accounting.
Assuming a KBA or Ramsar label creates enforceable rules
These designations can guide priorities and obligations, but their practical restrictions depend on the applicable national laws, agreements and management arrangements.
Using a TFCA boundary as though it were a single legal unit
Identify each component’s domestic status, authority and rules. Cross-border cooperation does not replace national legal instruments.
Equating community participation with equitable outcomes
Participation should be backed by documented consent, representation, benefit sharing, grievance procedures and monitoring of livelihood impacts.
Presenting draft norms as settled law
The 2026 OECM norms document is a draft invitation for comment. Check for a later final instrument before making claims about binding national requirements.
Quoting finance figures without their period and source
Keep the year, speaker, programme and basis attached to every number. Historical tax deductions, approximate benefits and multi-decade investment totals are not interchangeable metrics.
What the comparison means in practice
South Africa does not need one universal replacement for protected areas. It needs a portfolio in which each mechanism does the job it can perform well. Statutory protected areas provide the clearest legal durability. Stewardship can bring private and communal land into conservation through negotiated agreements and incentives. Conservation areas and partnership arrangements can connect working landscapes, but their security must be examined. OECMs can recognize effective conservation that occurs outside protected areas, provided the site passes an outcome-based assessment. KBAs guide priority setting, while biosphere reserves, Ramsar sites and TFCAs coordinate conservation at broader scales. Marine protected areas apply the statutory model to ocean spaces.
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The practical test is not which label sounds strongest. It is whether the chosen instrument has a legitimate governing authority, respect for rights and tenure, a credible management plan, sustained ecological results, transparent monitoring and financing that can last. Using those tests prevents both under-counting conservation that occurs outside national parks and over-counting sites that have biodiversity value but lack durable, demonstrable protection.
Frequently Asked Questions
Can private or communal land count toward South Africa’s conservation targets?
Yes, potentially. Private and communal land can contribute through a formally declared protected area, a stewardship arrangement or another mechanism. The applicable legal status, tenure security, governance, monitoring and outcome evidence determine how the site can be counted; ownership alone is not enough.
Does a stewardship agreement automatically make a site an OECM?
No. Stewardship includes protected-area, conservation-area and partnership categories. A non-protected site must be assessed individually against OECM requirements for governance, management and positive, sustained in-situ biodiversity outcomes.
Can a Key Biodiversity Area be reported as protected?
Not on the KBA label alone. A KBA identifies biodiversity importance and helps prioritise action, but it does not itself confer formal protection.
Are biosphere reserves and TFCAs OECMs?
Not automatically. Their component zones or sites retain distinct legal and governance arrangements. Any proposed OECM must be assessed at the relevant site level.
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